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BIOTECHNOLOGY,
PROPERTY RIGHTS AND THE ENVIRONMENT: TOWARDS A NEW LEGAL ORDER? Gerard
M.F. Snijders* II
D 1 Introduction ADifferences of opinion will be the
final blow for Avebe transgenic potato@, so reads the heading of a detailed background article
in the Agrarisch Dagblad of Saturday 4 August 2001. This article
describes the demise, after ten years, of a project by the Avebe potato group
which aimed to achieve large-scale cultivation of a potato developed in 1989 as
the result of genetic modification. This potato no longer contained amylose
starch, only amylose pectin starch. This was to simplify the processing of the
potato considerably, resulting in a substantial reduction of costs. Initially
cultivation was permitted – after just a few years about 200 Dutch farmers were
growing a total of some 1200 hectares a year – but, after the scientific
committee of the European Union had called the safety of the potato into
question in 1998, cultivation of the potato was banned in the year 2000. There
was the fear that because of the genetic modification used, the potato, once
released into the environment, could lead to resistance to kanamycine, an
essential antibiotic in the health care industry, and the chemical amykacine
derived from it. Both these products play an important role, particularly in
the treatment of serious pulmonary disorders and blood poisoning. There is
considerable debate among scientists about the legitimacy of this fear.
Stopping the project resulted in (direct) loss to Avebe of more than 8,000,000
Euro. The media often report on problems to do
with genetic modification. In the Agrarisch Dagblad of 26 June 2001, for
instance, we can read that the Dutch action group ADe Razende Hazen@ had
destroyed two experimental plots growing genetically modified sugar beet. It
concerned the variety Roundup-Ready, cultivated in a field trial by the
multinational Monsanto. On 29 June 2001, the magazine Oogst, the
mouthpiece of the Confederation of Agriculture and Horticulture LTO-Nederland,
reported that the Minister of Housing, Spatial Planning and the Environment
had rejected all 21 Dutch requests for field trials with genetically modified
crops, since the plots of land on which the trials were to take place had not
been sufficiently identified. The industries concerned considered appealing
against the decision in court. They objected to giving precise details of the
plots of land where the field trials were to take place, fearing that this
would lead to the destruction of the cultivated crops. Genetic modification arouses strong
emotions, but also leads to measures in the form of legislation. This
legislation may concern food safety, the labelling of products produced with
the aid of genetic modification, the protection of the environment in general,
and private property in particular. This report takes the protection of the
environment as the central theme. It contains a summary of prevailing Dutch law
in this area, whereby a distinction is made between public and private law.
Public law contains regulations for the protection of the general interest in a
clean and liveable environment. Private law protects the property rights of
individual citizens. 2 Public law 2.1 Legislation The
central legislation under public law in this context is formed by the
Genetically Modified Organisms Decree (Besluit genetisch gemodificeerde
organismen), hereafter referred to as the BGGO, which is based on Section
24 of the Hazardous Substances Act. The decree includes, among other things,
the implementation of the Council Directive 90/219/EEC of 23 April 1990 on the
contained use of genetically modified micro-organisms (OJ 1990, L 117, p. 1) and
the Council Directive 90/220/EEC of 23 April 1990 on the deliberate release
into the environment of genetically modified organisms (OJ 1990, L 117, p. 15).
Sections 2 to 22 inclusive concern the contained use; the introduction of
genetically modified organisms into the environment is provided for in Sections
23 to 35. Under the terms of Section 23 of the
BGGO, in principle the production, use, transport, possession, making available
to others, or disposing of genetically modified organisms is prohibited without
a permit from the Minister of Housing, Spatial Planning and the Environment.
Apart from contained use, there is an exception to this basic rule where the
Minister, according to an announcement in the Government Gazette, on the
grounds of a risk analysis as referred to in Section 24 subsection 2 of the
BGGO, has established that the activities concerned cannot have any undesirable
effects on man and the environment. In so far as aspects concerning the
protection of the environment are at issue, for which the Minister of
Agriculture, Nature Management and Fisheries is responsible, the latter must
also have agreed with this assessment. Furthermore, an exception is made for
activities with genetically modified organisms which, after a specific risk
assessment has been carried out as stipulated in accordance with part C of
Council Directive 90/220/EEC concerning contained use, have been marketed
within a member state of the European Union or another state that is party to
the European Economic Area Agreement, or with products that must undergo a
specific risk assessment under the terms of community legislation as referred
to in Section 10 subsection 1 of the directive. A permit must be applied for from the
Minister of Housing, Spatial Planning and the Environment. Under the terms of
Section 24 subsection 2 of the BGGO, a risk analysis must be submitted with the
application concerning the proposed activities. This analysis must contain the
following information at any rate – as summarized in Appendix 3: A. Concerning the mechanisms involved: a. A description of the organism or organisms,
with information on: – the harmfulness to other organisms, – the epidemiology, – the formation of toxic compounds and – the formation of surviving structures; b. the method of construction of the organism
or organisms; c. the origin of the DNA and RNA introduced,
with a description of the function and characterization of that DNA and RNA; d. the genetic stability of the organism and
the possibility for transfer of genetic material to other organisms; e. information on organisms that are the
ultimate target of the process, and the effects of the host on these target
organisms; f. a description of the abiotic factors
relevant to the survival of the organism or organisms; g. a description of the biotic factors that
are important for the growth and survival of the organism or organisms, and the
anticipated effect of the modified DNA on this; h. information concerning any changes that are
aimed at affecting the survival of the organism or organisms or the transfer of
genetic material. B Concerning the activity: a. a description of the location where
activity is carried out, with details concerning the situation and access for
persons and animals; b. a description of relevant changes that can
be expected in the near future in the vicinity of the location where the
activity is taking place; c. a description of the dispersal route of the
organism or organisms; d. a description of the ecosystem in which the
activity is carried out, and the anticipated effects on that ecosystem; e. the method and duration of the activity; f. the way in which the growth and survival
of the organism or organisms and the information referred to under 1d and 2d
can be monitored over time; g. the way in which emergency measures can be
taken, should harmful effects of the activity arise in the environment. If
the Minister believes that, in order to obtain insight into the potential
dangers for man and the environment, certain information may be required, he
may order the applicant to supply such information as specified by him
concerning the proposed activity. The assessment framework is formed by
that which is laid down in Section 26 subsection 2 of the Hazardous Substances
Act: AThe permit
maybe refused only to protect the interests of man and the environment@. The BGGO does not elaborate
further on this criterion, so that the Minister has to make decisions on a
case-by-case basis.[1] Under the terms of Section 26 subsection
3 of the Hazardous Substances Act, subsections 3.5.2 to 3.5.5 inclusive of the
General Administrative Law Act and Section 13.2 of the Environmental Management
Act apply to the preparation of the decision on the application. Briefly, the
relevant provisions of the General Administrative Law Act stipulate that the
draft decision must be sent to the applicant and the administrative bodies
concerned within twelve weeks of the application, after which it must be made
available for general inspection within two weeks. This will involve publishing
it in one or more national daily newspapers, free local papers, and in the
State Gazette, after which the administrative bodies concerned may give their
recommendations in relation to the decision to be taken, while anyone may lodge
their objections to the draft decision in writing within four weeks of its
publication. During this period, everyone has the opportunity to exchange views
on the draft and express their objections verbally upon request. If this
opportunity is taken up, the applicant must also be invited. Then the decision
is taken – in principle within six months of the application – whereby the
Minister is also required to state his considerations regarding the objections
raised. Restrictions and other types of regulations
may be attached to the issue of a permit (Section 26 subsection 4 of the
Hazardous Substances Act). Acting of his own accord or at the request of the
permit holder or other interested parties, the Minister may amend, add to or
revoke restrictions and regulations, impose additional restrictions or attach
regulations to the permit at a later date, or revoke the permit as such
(Section 24 subsection 4 BGGO). If such a decision is not made at the request
of the permit holder himself, the Minister will only proceed with such a
decision in the interests of protecting man and the environment. If the applicant or permit holder learns
of new information concerning risks that the genetically modified organisms or
their treatment may cause for man and the environment, he must inform the
Minister immediately. In addition, he must also take measures straight away
that are necessary to protect man and the environment (Section 25 BGGO). Section 26 of the BGGO obliges the
permit holder to inform the Minister of the risks to man and the environment
once the activity has been completed. There
is a Committee for Genetic Modification (COGEM), which advises the Minister on
the risks associated with the manufacture of and activities with genetically
modified organisms, as well as on the ethical or social aspects relating to
activities with such organisms. The
Dutch government considered submitting a proposal to the States-General in the
spring of 1992 for a specific Act to deal with all legally relevant aspects of
genetically modified organisms. The wish for this was largely the result of the
importance of proper harmonization of the legislation concerning this as a
subject considered important. However, based on an extensive analysis carried
out by the ministries involved, this was decided against. Ultimately the
government felt it better to acquire experience first with the legislative
frameworks already in place and those in preparation in the area of genetic
modification.[2]
Meanwhile the plan for separate, integral legislation would appear to have been
abandoned.[3] The
above shows that the introduction of genetically modified organisms and crops
in the Netherlands is regarded as a problem in terms of environmental law, for
which a solution is being sought – whether justified or not[4]
– based on legislation concerning hazardous substances. The law concerning
spatial planning does not play a role within this framework. 2.2 Case law Case
law as a result of Sections 23 to 35 of the BGGO is scarce. In a decision of 13
January 2000,[5]
the Administrative Law Division of the Council of State gave a limited
interpretation of the scope of the BGGO, to the extent that products C such as milk and meat – originating
from animals fed on genetically modified maize plants do not fall under the
BGGO since these products in themselves are not genetically modified organisms.
The damaging consequences to man resulting from the consumption of products
originating from animals fed with genetically modified maize, as feared by the
plaintiffs, could not be regarded as detrimental to man and the environment
because of the release into the environment of genetically modified organisms,
so that these consequences could not lead to an overruling of the decision to
grant the disputed permit. 3 Private law 3.1 Legislation Dutch
legislation has no specific regulations relating to the recognition and
protection of private property interests e.g. those of neighbouring property
owners where GMO technology is introduced on a farm. This means that as far as
this subject is concerned, we have to resort to (mutually coherent) general
rules regarding statutory property rights between adjoining properties on the
one hand, and unlawful acts on the other hand.[6] Under statutory property rights between
adjoining properties, the proprietor of a piece of land is prohibited from
causing a nuisance to proprietors of other pieces of land to an unlawful
degree, such as the spreading of noise, vibrations, odours, stench or gases, by
withholding light or air or withdrawing support (Section 5:37 of the Dutch
Civil Code). Infringement of a right, and acting or failing to act in conflict
with a statutory obligation or that which is socially customary in unwritten
law, is regarded as an unlawful act, all this subject to the existence of a
ground for justification (Section 6:162 subsection 2 of the Dutch Civil Code).
The literature also points out that Anuisance@ also means interference in the enjoyment of one=s own property, whereby ! leaving aside cases of damage to property ! normally speaking there would be no case of an
infringement of a right (namely: the property right) of the aggrieved party,
but a violation on unwritten rules; nuisance in general is unlawful under Dutch
law, because causing such nuisance contravenes an unwritten standard of due
care.[7] Depending on the circumstances,
unlawfulness may also originate from the violation of a statutory obligation.
This situation arises, for instance, where an owner of a piece of land
experiences nuisance as a result of the fact that the owner of an adjacent
property has infringed the prohibition as contained in Section 23 BGGO, and has
sown his land with a genetically modified crop without possessing the necessary
permit. A violation of a condition attached to a permit also constitutes a
violation of a statutory obligation.[8] According to the basic rule of Section
6:162 subsection 1 of the Dutch Civil Code, a person who is guilty of
committing an unlawful act is required to compensate for the damage or loss
that has consequently been caused to another person. However, there is no
obligation for compensation, if the purpose of the standard contravened was not
to protect against damage as or loss suffered by the aggrieved party (Section
6:163 of the Dutch Civil Code). In particular, not all cases of unlawful
nuisance lend themselves to claiming monetary compensation. However, instead of
compensation for damage or loss already or yet to be suffered, a prohibition
may be claimed on an unlawful act. An injuction on undertaking a future act
that is regarded as unlawful tends to be pronounced upon penalty of a fine.
Incidentally, a demand for such a prohibition can be refused by the court, if
such conduct, unlawful in itself, should be tolerated for reasons of important
social interests (Section 6:168 subsection 1 of the Dutch Civil Code). Such a
refusal does not affect the claims for compensation of those who are
disadvantaged as a result of the unlawful act. The court can impose a
prohibition at a later stage, if an order to pay compensation is not complied
with (Section 6:168 subsection 3 of the Dutch Civil Code). Although Sections 5:42, 5:44 and 5:45 of
the Dutch Civil Code contain provisions relating to statutory property rights
between adjoining properties that concern the presence of plants, these are not
relevant to the problem of genetically modified organisms; the issue there is
the distance from the plants to the property boundaries (in relation to the
height of such plants), overhanging branches, penetrating roots and the
ownership of fallen fruit. 3.2 Case law There
is no case law known from Dutch courts containing decisions on the
(un)lawfulness of sowing or planting genetically modified crops in relation to
neighbouring proprietors or land users. However, a few court decisions can be
mentioned that are important in this context. The relevant – but very broad –
criterion for assessing matters such as these was formulated in a ruling by the
Supreme Court of 1 May 1991.[9] Tree
nurseryman De Jong had a problem with weed seeds originating from the land
belonging to his neighbour, Van Tol. De Jong suffered damage, since he had to
weed the pots in which he cultivated the trees more frequently than would have
been necessary if Van Tol had kept his land clear of weeds. Was this a case of
unlawful nuisance, so that Van Tol was obliged to compensate De Jong for the
damage? The Supreme Court considered that the answer to the question whether
the causing of nuisance is unlawful – leaving aside any specific applicable
statutory regulations – depends on: Athe nature, the seriousness and the duration of the
nuisance and the resulting damage in relation to the further circumstances of
the case, including local circumstances A. The
Supreme Court then agreed with the view of the district court that Van Tol was
not cultivating his land any differently compared to the period before De Jong
set up business next to him. The district court had taken the nature, duration
and seriousness of the nuisance into account, and had also considered the fact
that the businesses of Van Tol and De Jong were in an agricultural area. In
this context, the court had rightly judged that there was no unlawful nuisance
– i.e. unlawful dispersal of seed – in this case. For our subject, the formulated standard
in particular is important. This standard was also applied after 1991 in
judging, for instance, the damage caused by the contamination of greenhouses
from neighbouring beehives.[10] In the
Supreme Court=s ruling of
15 February 1991[11],
following a case of damage by a colony of cormorants to fish farms, the
standards were set out as follows: AThe answer to the question whether the causing of
nuisance is unlawful – leaving aside applicable specific statutory regulations
that are not relevant in this case – depends on the nature, the seriousness and
the duration of the nuisance and the damage thus caused in relation to the
further circumstances of the case whereby, among other things, account must be
taken of the importance of the interests that are being served by the activity
causing the nuisance, and the possibility, partly in view of the related costs,
and the willingness to take measures to prevent damage or loss". It
is beyond doubt that the nature and (possible) seriousness of nuisance caused
by the wind dispersal of seed from a genetically modified crop are of a
completely different order to that of the dispersal of Anormal@ weed seed. It may be assumed that
the court will adopt very strict standards of due care in the case of a
cultivator of genetically modified crops, in view of (the lack of certainty of)
the associated risks. According to the ruling quoted here, in
assessing the damage, account must also be taken of the interests served by the
genetic modification on the one hand, and the possibility for preventive
measures on the other hand. The fact that a grower possesses a permit as
referred to in Section 23 BGGO does not imply that the dispersal of seed over
his neighbours is permitted.[12] There was indeed a case of unlawful
dispersal of weed seed in the ruling of the Court of Appeal of The Hague on a
case dated 18 February 1999.[13] The legal
person under public law Staatsbosbeheer (the Dutch Forestry Commission)
was the manager of >t
Ganzey nature reserve. In the interests of the nature
development plan considered desirable there, the rough land was left unmown and
the grazing of the rest of the land belonging to the nature reserve was
reduced. As a result, owners of adjacent land experienced nuisance, including
Breukink, the plaintiff in the proceedings. Breukink was confronted in
particular with the dispersal of seed panicles from field thistles on to his
land.[14]
In order to combat the effects of this, he was forced to incur extra costs. The
court ruled that Breukink had to tolerate the way in which Staatsbosbeheer
managed the nature reserve, weighing up the nature interest entrusted to Staatsbosbeheer
on the one hand, and the interests of Breukink on the other hand, Staatsbosbeheer
could have decided in all reasonableness that the development of the nature
reserve they wished for would take precedence. Consequently, the method of
management was not prohibited in the future. Nevertheless, Staatsbosbeheer
acted unlawfully towards Breukink, if and for as long as the organization
failed to compensate him for the loss caused to him as a result of the
management of the nature reserve. After all, the detrimental effects of a
decision taken by a government organization must not be disproportionate in
relation to the objectives served by the decision. The court ruled that the
damage suffered by Breukink was disproportionate, in so far as it exceeded the
damage that had to be attributed to normal business risk. Business risk
included the damage that Breukink had to take account of in relation to general
(social) developments. The court subsequently considered that
an owner of an agricultural business situated in an area such as the one in
question must take account of the fact that, in view of current social
developments, a nature reserve exists or is to be created in the (wider) vicinity,
the management of which gives a higher chance of nuisance from weeds, but not
that such management is carried out on the neighbouring plot of hand. The significance of this ruling for our
subject is difficult to judge. It does not constitute a ruling of the highest
court in these types of matters, while the decision is dictated by a variety of
factual circumstances. Furthermore, the dispersal of seed from the field
thistle as a consequence of a certain method of nature management by a
government organization (such as Staatsbosbeheer) cannot be compared
automatically with C for
example – the dispersal of seed from a genetically modified crop as part of a
field trial, whether by a government organization or a private seed breeder.
However, the ruling does show clearly that there can be tension between the
interests of the parties affected by seed dispersal. Such tension can be
removed by allowing the one party to continue his trials Ain the public interest@, while the other party is entitled
to compensation for the harm he subsequently suffers. In fact, the ruling
provides an illustration of the system already discussed in the aforementioned
Section 6:168 of the Dutch Civil Code (although there, nothing less than Asubstantial social interests@ are referred to). The case law quoted concerned particular
cases, each of which involved an individual citizen or legal person acting as
plaintiff. Dutch law, however, also allows for the possibility of collective
action (Section 3:305a of the Dutch Civil Code). This means that in a case of
unlawful nuisance, a body such as a nature conservation organization may appeal
to the courts. In that case, the organization cannot claim monetary
compensation; such a demand may only be made by an individual aggrieved party
(Section 3:305a par. 3). The demand for a prohibition is an option although, as
already discussed, it may fail against that which is laid down in Section 6:168
of the Dutch Civil Code. In order to be successful in bringing
any claim to court, by whichever plaintiff, each time the condition applies
that the plaintiff must have sufficient interest in the matter; without
sufficient interest, no-one will be granted a legal claim, according to Section
3:303 of the Dutch Civil Code. 4 Summary and conclusion The
Netherlands has no integral legislation regarding genetically modified organisms,
only a number of regulations concerning specific aspects. In so far as there
are regulations under public law that concern the protection of the
environment, these encompass the implementation of the EC directives concerned.
The regulations have been brought about within the framework of legislation in
respect of hazardous substances. As far as protection under private law
is concerned, although in theory other possible legal bases can be cited, in
effect we must fall back on the (mutually coherent) regulations concerning
statutory property rights between adjoining properties and unlawful acts. The
central question is, as always, whether a type of behaviour can be considered
as unlawful nuisance. Leaving aside the case of malicious damage to property,
unlawful nuisance is said to exist if written or unwritten law (i.e. a standard
of due care) is violated. Whether a violation of unwritten law has occurred
will depend on ! in the
words of the Supreme Court ! the
nature, the seriousness and the duration of the nuisance and the damage thus
caused in relation to the further circumstances of the case, whereby account
must be taken, among other things, of the importance of the interests that are
being served by the activity causing the nuisance on the one hand, and the
possibility, partly in view of the related costs, and the willingness to take
measures to prevent damage or loss on the other hand. Case law on this subject is scarce. In
particular, no rulings are known of Dutch courts, in which a decision has been
made on the (un)lawfulness of the sowing or planting of genetically modified
crops in relation to neighboring proprietors or land users. It may be assumed
that the court, in view of the (lack of clarity of the) associated risks, will
apply strict standards of due care. A case may arise where the causer of the
unlawful nuisance is obliged to compensate for the subsequent damage or loss
caused, while a demand for a prohibition will be refused for reasons of
important social interests. Notes * University of Nijmegen, Attorney
at Wijn & Stael, Utrecht. [1]. H.J. Bronkhorst en W.J.E. van der
Werf, Genetische modificatie in de landbouw (Genetic modification in
agriculture), Land- en Tuinbouw Bulletin, 2001/0 1, p. 19. [2]. See here the Explanatory Memorandum
to the Decree for the amendment of the BGGO dated 3 July 1992, Bulletin of
Acts and Decrees 1992, 376. For the results of the analysis, see the Parliamentary
Documents II 1991/1992, 22300 XI, no. 11. [3]. S.J.R. Bostyn & co., Moderne
biotechnologie en recht, (Modem biotechnology and law), Recht en Praktijk
85, Kluwer, Deventer, 2001, p. 22-23. [4]. In his note to the decision of the
Chairman of the Administrative Law Division of the Council of Sate of 22 March
1994, AB 1994, 446, Drupsteen put the question whether the Hazardous
Substances Act indeed provides an adequate basis for the BGGO, since organisms
(as part of the animate world) cannot be regarded as belonging to the
substances and preparations (as part of the inanimate world) for which rules
may be set under the terms of Section 24 of the Act. See also H.E.J. van der
Meulen, Biotechnologie en het Besluit genetisch gemodificeerde organismen (Biotechnology
and the Genetically Modified Organisms Decree), Milieu en Recht, 1997,
p. 127-128. [5]. Published in AB 2000, 95. [6]. In theory, other bases for a claim
are conceivable. In particular, reference can be made in this context to the
regulations of product liability in Sec. 6:185 to 6:193 inclusive of the Dutch
Civil Code, whereby Council Directive 85/374/EEC (OJ 1985 L 210, p. 29) was
implemented. However, generally speaking these regulations will not provide
much consolation, since genetically modified organisms that have given rise to damage
as discussed here have not usually been >put into circulation= within the meaning of the directive, while there
need not be defective products, nor a form of damage against which the
directive aims to offer protection. Moreover, a claim has a substantial chance
of failing against the plea of >state of the art= permitted under Dutch law. For a detailed discussion of
this, see L. Bergkamp, Allocating unknown risk: Liability for Environmental
Damages Caused by Deliberately Released Genetically Modified Organisms, Tijdschrift
voor Milieu Aansprakelijkheid, 2000, p. 104-105. See also liability for
faulty goods (Sec. 6:173 Dutch Civil Code), hazardous substances (Sec. 6:175
Dutch Civil Code) and animals (Sec. 6:179 Dutch Civil Code). In relation to
this, see E.A. Messer, Aansprakelijkheid voor genschade (Liability for
gene damage), Nederlands Juristenblad, 1992, p. 285-293. [7]. W.J.M. Davids, Burenrecht (statutory
property rights between adjoining properties), Monographs in the New Dutch
Civil Code B26, Kluwer, Deventer, 1999, p. 20-21. See also Asser-Hartkamp
4-Ill, no. 38-40 and Asser-Mijnssen-Davids-Van Velten, no. 39-43. [8]. Incidentally, the reverse does not
automatically apply; under Dutch law an act causing damage or loss is not
lawful by definition, simply because the person committing the act had the
necessary permit to do so. A permit holder too must continually ask himself to
what extent due social care restricts his freedom of action. See
Asser-Mijnssen-Davids-Van Velten, no. 42. [9]. Published in NJ 1991, 476. [10]. Supreme Court 28 April 1995, NJ
1995, 513 and Supreme Court 18 September 1998, NJ 1999, 69. [11]. Published in NJ 1992, 639. [12]. See footnote 8. [13]. Published in NJ 2000, 202. [14]. The dispersal of the seed panicles of
this weed have given rise to disputes on numerous occasions. For a similar
case, see the Court of Appeal at >s-Hertogenbosch 5 February 1990, NJ
1990/645. Cite as: Gerard M.F. Snijders, Biotechnology, Property Rights and the Environment: Towards a New Legal Order?, vol 6.4 ELECTRONIC JOURNAL OF COMPARATIVE LAW, (December 2002), <http://www.ejcl.org/64/art64-9.html> |
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