Uitspraak
THE HAGUE COURT OF APPEAL
1.Fidelis Ayoro OGURU,
Alali EFANGA,
VERENIGING MILIEUDEFENSIE,
mr.Ch. Samkalden of Amsterdam,
1.SHELL PETROLEUM N.V.,
THE “SHELL” TRANSPORT AND TRADING COMPANY LIMITED,
mr.J. de Bie Leuveling Tjeenk of Amsterdam,
1.the legal person incorporated under foreign law ROYAL DUTCH SHELL PLC.,
SHELL PETROLEUM DEVELOPMENT COMPANY OF NIGERIA LTD.,
mr.J. de Bie Leuveling Tjeenk of Amsterdam.
locus standiin the class action and in which (iii) the 843a Code of Civil Procedure claims of MD et al. were partially allowed;
mr.B.E. ter Haar concerning the confidential documents filed by Shell. Shell also submitted those documents on a USB flash drive.
1.The facts
Estimated quantity of oil spilled: 400 BBLS’ (400 barrels of 159 litres each). Part B of the report includes the following, inter alia.
Report on Recovery, Clean Up and Remediation Project at 20” Kolocreek-Rumuekpe Trunkline at Oruma(hereinafter: the Clean-Up report) for the SPDC.
Clean-Up and Remediation Certification Format(hereinafter: the Clean-Up certificate), which was signed by three Nigerian government institutions, for the decontamination of the pollution at Oruma. The following, inter alia, is stated in this certificate:
2.The claims of MD et al. and the judgments of the district court
3.The appeal; preliminary considerations
lex causae(in this case: Nigerian law), as well as the substantive law of evidence, as currently expressed in Book 10 Section 13 Dutch Civil Code, including special rules on the division of the burden of proof relating to a certain legal relationship and which seek to specify the subjective rights ensuing from that legal relationship. In all other respects, the division of the burden of proof, as well as the obligation to furnish facts, is governed by the
lex fori, in this case Dutch law, more specifically Dutch procedural law.
ex nunc). Feature B) is specifically pertinent in the situation that the claim was dismissed in the first instance, such as is the case here.
Gazprombank)), so that the reciprocity requirement from the aforementioned Nigerian act cannot be viewed as a hindrance to recognition of this ruling’s decision on claim III.a in Nigeria.
Military Governor of Lagos State v Adebayo Adeyiga), the Supreme Court considered as follows (p. 26):
restoration of things’), which also covers a continuing unlawful omission. Nigerian law also has a declaratory decision, known as declaratory relief, as equitable remedy, see Supreme Court 13 April 2007, S.C. 243/2001 (
Ibator v. Barakuro).
in fine, the ‘normal’ division of the burden of proof must be determined based on Dutch law as the
lex fori, meaning in accordance with Section 150 Dutch Code of Civil Procedure, which states as the main rule that the party invoking the legal effects of the facts or rights alleged by said party carries the burden of proof as regards the respective facts or rights.
Compensation’), stipulates the following, inter alia:
Abubakar v Joseph) (Appendix 1 to Exhibit 19), legal ground 14 on p. 317, legal ground 20 on p. 318 and p. 341 – except in the case of
res ipsa loquitur, a common law principle explaining that the mere occurrence of an event implies negligence, without direct or further evidence being required. In the aforementioned ruling, the following was further stated on the meaning of negligence (legal ground 12 on p. 316/p. 350):
Caparo Industries plc v Dickman) – from which the name of the Caparo test is derived – states the following about the proximity requirement (p.633):
recommendations’ reflecting the ‘
industry custom’ (Exhibit M.1, no. 60). It is obvious to assume, also according to the common law such as it is applied in Nigeria, that such non-binding standards – depending on their nature and contents – may aid to specify or illuminate a duty of care. This is confirmed in point 50 of the opinion M.T. Ladan and R.T. Ako of 13 December 2011, submitted by MD et al. as Exhibit L.1.
Ryland v Fletcher(House of Lords 17 July 1868, (LR 3 HL 330)). The court of appeal in that case described that rule as follows:
non natural use’ of the land. The
Rylands v Fletcherrule imposes strict liability – which incidentally is not unlimited – on the occupier of the land for the damage that occurs if the conditions of this rule are met. The strict liability of Section 11(5)(c) OPA can be viewed as the implementation of this rule in case of pipe damage.
Bodo v SPDC) in which (in legal ground 64) that exclusivity of the OPA is assumed;
Nigerian Agip Oil Co v Ogbu) (Exhibit 61, Appendix 2) in which on p. 29 in an
obiter dictum, referencing inter alia
Bodo v SPDC, it is noted that Section 11(5) OPA has set aside the common law;
Johnson v SPDC) (Exhibit 61, Appendix 4) in four consolidated cases in which it was determined that the OPA ‘
has provided a comprehensive compensation regime’.
Bodo v SPDC,the Nigerian courts did not view the OPA, or Section 11(5) OPA, as exclusive. This is apparent from, for example, the ruling in the case
SPDC v Otoko(Court of Appeal 25 May 1990, [1990]6 NWLR 693) (Exhibit J.5). This case concerned leaks from pipelines, so that that case (also according to Shell; point 291 DoA/SoA-cross/2) fell within the OPA’s scope of application. Nevertheless, the Court of Appeal did not apply the OPA but rather common law (tort of negligence) (see, inter alia, points 19 et seq. of the dictum). In the ruling in the case of
SPDC v Edamkue(Supreme Court 10 July 2009, 14 NWLR (Pt. 1160) 1; (2009) 6-7 S.C. 74) (Appendix 1.12 to Exhibit M.1)) the common law rule of
Rylands v Fletcherwas used in a case regarding a pipeline leak. In a ruling (Supreme Court 5 June 2015, LOR (5/6/2015/SC) (
SPDC v Anaro)delivered after
Bodo v SPDC, the Supreme Court determined in a case which (also according to Shell; point 291 DoA/SoA-cross/2) fell under the scope of application of the OPA, that the
Rylands v Fletcherrule was rightfully applied (Exhibit Q.24, see mainly p. 13 of said ruling). From this it can be deduced that the Supreme Court did not view the OPA as exclusive, both before and after
Bodo v SPDC. A Federal High Court (14 December 2016 (
Ajanaku v Mobil) (Exhibit Q.23) considered as follows: ‘
It is settled law that victims of oil operations spillage/damage can maintain an action for compensation under the rule in Rylands vs. Fletcher’.
Bodo v SPDC, and was later sporadically used by lower Nigerian courts, but not by the Supreme Court, which continued to assume its non-exclusivity. In view of the system of precedent, this court must follow the Supreme Court. All the more so now the only higher Nigerian court has assumed the exclusivity, the Court of Appeal in
NAOC v Ogbu, namely in an
obiter dictum(see, inter alia, point 37 of the opinion of Shell’s expert F. Oditah in Exhibit 61), which has no binding effect (see Uniken Venema/Zwalve,
Common Law & Civil Law, 2008, p. 80). Therefore, Shell’s argument as stated under 3.22 does not succeed. The OPA is not exclusive, so that common law legal actions are also an option, with the associated legal and equitable remedies.
Chandler v Cape) (Exhibit 25), in which in substantive proceedings the liability of the parent company with respect to employees of the subsidiary was assumed;
Okpabi v RDS) (Exhibit Q.34), in which in the context of the competence issue it was determined that the claimants had no arguable case against the parent company (appeal before the Supreme Court pending, case id: UKSC 2018/0068));
Vedanta v Lungowe), in which the opinion in the context of the competence issue, that claimants had an arguable case against the parent company, was upheld.
Chandler v Cape’ case referred to under 3.28, added by the Court)
, the subsidiary inherited (by taking over a business formerly carried on by the parent) a system for the manufacture of asbestos which created an inherently unsafe system of work for its employees, because it was carried out in factory buildings with open sides, for which harmful asbestos dust could, and did, escape. As a result, and after a full trial, the parent was found to have incurred a duty of care to the employees of its subsidiary, and the result would surely have been the same if the dust had escaped to neighbouring land where third parties worked, lived or enjoyed recreation. (…).
Vedanta v Lungowe(hereinafter: the
Vedantarule) means that it must be assessed according to the usual standards – the
Caparotest, see legal ground 3.18 – whether or not a parent company has a duty of care with respect to third parties that have a relationship with its subsidiary, that a further classification in
Fallgruppenis not applicable, and that involvement in the subsidiary is a basic condition (cf. point 8 WS/2-S). Point 80 of
Chandler v Capestates as an extra condition for a duty of care of the parent company that the parent company knew or should have known about the unsafety of the system used by the subsidiary. This knowledge requirement must be deemed to form part of the
Vedantarule. If the parent company is not aware or should be aware of the injurious acts of the parent company, it is difficult to recognize that, as far as the parent company is concerned, the foreseeability requirement – step a) of the
Caparotest – has been met nor that it would be fair, just and reasonable – step c) of the
Caparotest – to impose a duty of care on the parent company.
Vedantarule may be represented as follows: if the parent company knows or should know that its subsidiary unlawfully inflicts damage on third parties in an area where the parent company involves itself in the subsidiary, the starting point is that the parent company has a duty of care in respect of the third parties to intervene.
Vedanta v Lugoweruling, there is no reason to assume that the Nigerian court would not adopt the
Vedantarule, as shown above. Therefore, this rule must be deemed to form part of Nigerian law. Since Nigerian law is identical to English law in this respect, it would make no difference whatsoever if the parent company liability were to be assessed not according to Nigerian law (see legal ground 3.26) but to English law.
4.Preliminary defences of Shell
condition precedent. The Court will now assess/further assess, in the aforementioned order, the preliminary defences on which no definitive decision has yet been taken.
any person suffering damage’. The words ‘
any person’ show that the group of persons with a right of action is very broad and that no specific requirements are set as to the capacity of the injured party. This does not tally with expecting an injured party that is able to prove that they have the capacity of owner or (lawful) user – which is not required – to also demonstrate how they acquired the ownership or right of use. The same applies to a claim on the basis of negligence. This also does not require specific requirements as to the capacity of the injured party. Insofar as the claims of Oguru and Efanga are based on Section 11(5)(b) and (c) OPA and the tort of negligence, Shell’s argument a) does not succeed for these reasons alone. Whether or not this argument is applicable to the other bases of the claims of Oguru and Efanga needs no consideration, in view of the considerations in 5.30, 6.29, 8.29 and 9.6.
are owned and used by’ Oguru and Efanga with ‘
the right to do so’ (hereinafter: the M.4 statements). On appeal, in DoA-cross/2, MD et al. have submitted survey plans with maps of 4 October 2019 as Exhibit Q.59 (A and B), on which is stated: ‘
shewing property area’ of Oguru and the deceased Efanga. The land and the fish ponds are depicted in red lines on the maps. According to the assertions of MD et al. in point 31 WS/2-MD, following on from points 92 and 106 DoA-cross/2, a survey plan is an official, certified document on which the location and demarcation of a piece of land is depicted, comparable to a cadastral map in the Netherlands. Shell has not contested this. From the last sentence of point 61 WS/2-S, it can be deduced that Shell deems the M4 statements to be incorrect, because the map associated with the statements show the lands and fish ponds at different locations than on the map of the survey plan, which Shell apparently does deem to be correct. In point 92 (with note 102) DoA-cross/2 and point 17 WS/2-MD, MD et al. have given a credible explanation for this, namely that the person who drew the circles on the map of the M.4 statements had mistaken a path between the lands of Oguru and Efanga for the right of way, and that if the map of the M.4 statements is turned 45º to the right, it is clear that it corresponds with the maps in the survey plans, as is made clear with the photograph on p.8 WS/2-MD. Regardless, it is at any rate sufficiently clear from the not-contested survey plans where the lands and fish ponds of Oguru and the late Efanga are situated, and that they in any case were the users of the lands and the fish ponds (
‘property area’). Therefore, argument b) also does not hold.
spillpoint). It appears from the scale of the map that Oguru’s land starts at about 100m from the spillpoint and that Efanga’s land borders it. The land and fish ponds of Oguru and Efanga are situated so close to the location of the leak that, also in light of the considerations in 3.34, the oil flow inevitably reached those lands and fish ponds and at least covered parts of the lands and fish ponds, also considering that Shell has not asserted that the oil almost exclusively flowed in the opposite direction. It can therefore be considered certain that Oguru and Efanga incurred at least some damage as a result of the leak. Shell’s argument c) also does not hold.
condition precedent) set out in the last sentence of Section 11(5) OPA, in conjunction with Sections 11(6) and 20(2) OPA, to be able to claim compensation at law based on that condition, namely that the parties must have first consulted each other in an attempt to reach agreement on the amount of compensation. MD et al. counter this with the statement that the OPA does not contain such a
condition precedentand, in the alternative, that it cannot be alleged against them since the amount of compensation is not yet at issue (points 14 and 21-32 DoA-cross/2).
any dispute as to whether any compensation is payable under any provision of this Act’ and ‘
any dispute’ ‘
as to the amount thereof’. The last sentence of Section 11(5) OPA, containing the alleged
condition precedent, only pertains to disputes on ‘
the amount of such compensation’. Claims I and III.a-a, which are partially based on the OPA, are for declaratory decisions with a referral to follow-up proceedings for the determination of damages, and declaratory decisions as a prelude/basis for future claims for compensation, respectively. Those claims therefore pertain to disputes about the question ‘
as to whether any compensation is payable’ and not, or not yet, about the question of ‘
the amount of such compensation’. The alleged ‘
condition precedent’ does not come into play here. Therefore, MD et al. have rightfully put forward that this cannot be alleged against them.
under no obligation is to compensate your clients for the damage claimed (…)’. During the appeal proceedings, the Court repeatedly requested/urged the parties to examine whether or not they could reach a mutual agreement (see, inter alia, p. 6 of the record of appearance of the parties of 24 November 2016 and p. 18 of the RH-2020). At the 2020 hearing, Shell noted that a settlement is not an option – as the Court understands it: for Shell – because MD also seeks to protect the interests of three communities, including the Oruma community, and not just those of several individual claimants. Taking all this into account, Shell effectively halted ahead of time the consultations it now emphasizes so much. Considering this state of affairs, the condition precedent must be deemed as fulfilled, in view of the underlying principle, as regards Dutch law, of Book 6 Section 23 subsection 1 Dutch Civil Code.
5.The claims in respect of ‘Origin’ (of the leak)
in fine). However, it is in dispute which evidence evaluation standard (threshold of proof) applies here: is that the special standard for civil cases, beyond reasonable doubt, such as MD et al. believe, or the regular standard of preponderance of weight of evidence, such as Shell believes?
SPDC v Edamkuecase of 2009, referred to in legal ground 3.23, the beyond reasonable doubt standard was used in a civil oil leak case in which third-party sabotage was invoked, as the Court understands. This is not out of the ordinary considering Section 138 subsection 1 of the Evidence Act 1945.
SPDC v. Firibeb) (Appendix 1 to Exhibit 60)) regarding Section 11(5)(b) and (c) OPA it becomes clear that in the first instance, the Federal High Court ruled (p. 8): ‘
I do agree (…) that the standard of proof required for claims of vandalisation and acts of a third party are high. Vandalization and acts of a third party conno[n]tes criminality and the standard of proof required is beyond reasonable doubt’. On appeal in that case, the SPDC did not submit grounds for appeal against this judgment.
SPDC v Okeh) (Exhibit Q.60, Appendix A) also concerned third-party sabotage. In an explanation of the law on p. 436/437, reference is made to the beyond reasonable doubt standard from
SPDC v Edamkueand to Section 138(1) of the Evidence Act. From this it can deduced that this Court of Appeal effectively applied the beyond reasonable doubt standard. The fact that on p. 439, second paragraph, mention is made of reliable proof does not take away from this, especially not since that paragraph emphasizes that in that case there was actually no proof at all for sabotage (‘
little or no iota of proof‘).
I entirely agree with the submission of (…) that allegations of crime in civil matters must be proved beyond reasonable doubt and specially pleaded and particularized’. It was then determined that this threshold had been met.
Compensation claims relating to cruel oil spillage & land acquisitions for oil & gas fields in Nigeria (A Suggested Practice Guide), Peral Publishers, 2011, p. 315 (Exhibit Q.14) the following can be read:
temptation for civil courts’ to interpret Section 138(1)/135(1) Evidence Act in a way that requires beyond reasonable doubt, also in cases of non-party sabotage. The Court finds that under applicable Nigerian law, as it is applied by the Nigerian courts, this high threshold of proof must be applied in third-party sabotage cases. The fact that Oditah and Ayoola deem this incorrect, does not alter this. The opinions of these party experts carry insufficient weight in relation to the legal practice, as is evident from 5.6 through to 5.9.
lex causae(see legal ground 3.1), because it is closely related to substantive law. Unlike argued by Shell, inter alia, in points 11-14 WS/2-S, it is not the case that in a situation like this, whether special or not, the threshold of proof to be applied is determined by Dutch law as the
lex fori.
Magnetic Flux Leakage(MFL) technique – with a type of robot (a so-called intelligent pig) which moves through the pipeline and inspects it from the inside (a pig run, also known as an inline inspection (ILI) run), which results apparently proved that at the time (six months before the leak) the pipe showed no thinning at the location of the leak, so that it would not seem logical that the damage to the pipeline was due to corrosion.
is now very low’ (p. 16, second paragraph), which is more in line with Shell’s interpretation. A further analysis of the experts’ report shows the following (references pertain to the final report, unless stated otherwise).
clearly’ state where the 2005 leak is located (p. 11, final paragraph), namely at 7749.68-7750.04 meters downstream from the Kolo Creek manifold (p. 8, seventh asterisk in conjunction with p. 7, second asterisk). They also specified the position of the leak at 07:55 hours while the JIT report stated 08:30 hours, see p. 8 seventh asterisk. The experts also plainly established that external corrosion could not have caused the leak, which leaves only internal corrosion or external interference as potential causes, with the proviso that external interference ‘
by plant machinery and tractors etc’ (probably) is also excluded, so that, in the end, only internal corrosion and sabotage remain as the possible causes, or so the Court understands (p. 12, seventh paragraph; p. 18 point 3).
of very poor quality’ (p. 12, third paragraph): it is not detailed enough, does not have good photographs and generally does not meet the standards set to such a report (p. 16, third paragraph). The experts also find the JIT’s UT measurements ‘
questionable as to their accuracy’ (p. 12, fifth and sixth paragraph; p. 16, third paragraph) because due to the corrosion found in the pipeline (see under 5.21 below) the measurements should have revealed a greater variation in wall thickness. Therefore, the Court understands that the experts answered question 2 about the cause of the 2005 leak based solely on the information they obtained from the ILI runs of 2005, 2011 and 2016.
the 6 o’clock position’, but that for the first 15 km, where the Oruma leak occurred (see legal ground 5.18, first sentence) the depth of it was in ‘
general’ less than 40% (p. 10, last paragraph; p. 12, sixth paragraph). Based on ‘Z’, the experts also came to the conclusion that it is clear that the area around the position of the leak was ‘
clean’, ‘
with no corrosion evident around the leak’ (p. 16, fifth paragraph). This concerns the situation in the direct and wider vicinity of the leak.
‘at’the place of the leak there could be three
‘defects’; this was, according to the experts in their draft report, implied by the ILI reports, which at the same time indicated no ‘
significant areas of internal corrosion’ ‘
at the position of’ the leak, and which, still according to the experts in their draft report, in this respect provided conflicting information (see p. 13, third and fourth paragraph of the draft report B-D 12). Shell then noted that these concerned two ‘
minor indications’ which were the result of corrosion and one ‘
larger indication’, which is the leak this case revolves around (B-D 13, p. 27 under 2). On p. 8, seventh asterisk of the final report, this remark by Shell was apparently accepted as correct on the basis of the statement of Rosen B-D 14 Exhibit A (= AJ), which ‘
suggests that the additional corrosion features under the repair clamps are very low level ≤ 10%’. This solves the problem of the conflicting information.
the most likely cause of the leak is external interference rather than corrosion’ (p. 16, sixth paragraph). On p. 18, point 4 of the final report, the same was stated in slightly different wording: ‘
it is our impression that everything we have seen points to external interference as being the likely cause of the leak’. This conclusion/impression was already present in the draft report B-D 12, in identical wording (p. 14, second paragraph; p. 16, point 4). The Court understands that the experts’ thought process behind this conclusion/impression is that, since underneath the clamp (not the place of the leak) a very small amount of corrosion was found, in the direct vicinity of the leak no corrosion was found and in the wider area of the leak at best less deep corrosion was found, it is not likely that (underneath the clamp) at the location of the leak corrosion had developed so deep that it caused a hole.
to absolutely confirm’ that the leak was caused by sabotage is to remove the clamp from the leak, re-examine the leakage area, and drawing up a high-quality report, containing good photographs and research information (p. 19, third bullet point of the final report; p. 16 at 5, 5th bullet point of the draft report B-D 12). The Court understands that the experts’ intention was to convey that although the information about the corrosion situation in the immediate and wider vicinity of the place of the leak could reveal something about the probability of the existence of deep corrosion at that location (indirect information), but that a definitive answer can only be obtained with information about the leak itself and the place of the leak, such as photographs and measurements (direct information), which Shell has not provided.
latest ILI data supplied by Shell on 16 October 2018’ refers to the statement of Rosen B-D 14 Exhibit A, designated as AJ in the expert opinion. B-D 14 Exhibit A/AJ was only raised in the expert opinion as a solution to the ‘conflicting information’ issue flagged in the draft report (see legal ground 5.22) – except to justify the focus on the 2016 ILI run (see legal ground 5.20), which is not relevant in this context. Against this background, the passage cited above must be understood as follows: even though a complete picture cannot be obtained due to the lack of good photographs and measurements, ‘
the latest ILI data supplied by Shell on 16 October 2018’ ‘
however’ provide sufficient data to resolve the problem of the conflicting information to such an extent that the doubt, raised by the problem, is (‘
now’) very low. In view of this and considering the solving the ‘conflicting information’ problem has not lead to an adjustment of the conclusion/impression mentioned in legal ground 5.23 – which, after all, was already stated in the draft report using the same terms – the remark that ‘
doubt is now very low’ cannot be considered as a refinement of the conclusion/impression.
In the alternative: insufficient security of the pipeline’. In point 214 SoA/2, MD et al. have stated that when it is established beyond reasonable doubt – as the Court understands: only when – sabotage was involved, a further investigation is needed to establish whether or not ‘Shell’ was negligent in the prevention of the sabotage. From this the Court deduces that the assertions of MD et al. regarding negligence of the SPDC and the Shell parent companies to sufficiently secure, or have secured, the pipeline against sabotage, were brought to bear in case/under the condition that sabotage has not been proven beyond reasonable doubt. Since this condition has not been met, the assertions of MD et al. can remain undiscussed.
Rylands v Fletcherrule in light of the considerations in 5.28 and 5.29. Incidentally, the claims would not have been allowable based on the torts of negligence, nuisance or trespass to chattel, because as is apparent from legal ground 5.27, sabotage – although not proven beyond reasonable doubt – rather than overdue maintenance is the most likely hypothesis for the origin of the leak, so that it cannot be determined that the leak was due to negligence or unreasonable acts of the SPDC.
in fine). But it has not been proven, as explained in legal ground 5.30. This means that claims I and III.a-a in respect of Origin are not allowable against the parent company/companies.
Rylands v Fletcherrule. In the context of parent company liability, the burden of proof rests on MD et al. rather than on Shell.
6.The claims against the SPDC in respect of ‘Response’
in fine, 6.1 and 6.6
in fine).
– In the event third-party intrusion results in an immediate rupture, the intrusion alarm, coupled with a release alarm, will allow response to occur more quickly, and potentially reducing the volume released significantly.
Detecting and Minimizing Unintended Pipeline Releases’. Subsection 10.3.2 ‘Types of Release Detection Systems’ states the following, inter alia:
. Software for this system incorporates two independent methods of release detection: pressure point analysis and mass balance. Pattern recognition algorithms that distinguish normal operating events from leaks are used. When used with a communications system, pressure point analysis can provide the calculated location of a release.
specifies the requirements and gives recommendations for the application of Leak Detection Systems’ (p. 4). On p. 6, under the heading ‘
Requirement (…)’, it is stated that ‘
[a]n LDS reduces the consequences of failure by enabling fast emergency response’. The following text can be found on p. 9, under the heading ‘
Selection Of A Leak Detection System’:
and the physical sighting of leaks by the communities, Bristol pilots and other third parties (…).
Caparotest must be met, that is to say that the damage must be foreseeable, there must be proximity, and the duty of care in this case must be fair, just and reasonable (see legal ground 3.18).
was also classed as caused by outside interference’. As is apparent from p. 8, eighth asterisk, of the experts’ report, the 2004 ILI report mentioned no less than 129,678 corrosion spots in the Oruma pipeline, 37 of which had a depth of 40-59%. Even when allowing for a correction that can be made in connection with the 2016 ILI report (p. 11, paragraphs 4 through to 6 of the experts’ report), it must be concluded – concurring with the experts on p. 18, point 5 of the report – that internal corrosion was a serious problem in the Oruma pipeline, and was already present in 2004. In view of this, it was foreseeable for the SPDC before the 2005 leak that this specific pipeline would be affected – again – by a leak due to either insufficient maintenance/corrosion or sabotage. This is confirmed in a 2004 SPDC report (Exhibit M.3) about the Kolo Creek-Rumuekpe pipeline (this is the Oruma pipeline, see legal ground 1.d), in which it is noted that from SPDC investigations it had become clear that this pipe was ‘
likely to leak before the year 2003/2004’ (p. 2-17 of Exhibit M.3) and which also states the following (Exhibit M.3, p. 2-24):
SPDC shall:
Peace and Security in the Niger Delta; Exhibit C.7, see point 298 IS) contains the following passage (p. 13):
Shell Companies in Nigeria’ (see p. 4). In point 32 DoA/SoA-cross/2, Shell states that access was ‘regularly’ refused by the local population. In point 300 IS, MD et al. state that also in the case of Oruma it was to be expected that the SPDC would not immediately be given permission to access the leak. Shell has failed to contest this assertion sufficiently clear. Based on this, the conclusion must be that it was foreseeable for the SPDC before mid-2005 that it would not be allowed access, or with a delay, to a leak in the Oruma pipeline.
fair, just and reasonable’ to require the SPDC to have installed an LDS on the Oruma pipeline before the 2005 leak. The proximity requirement has also been met now that Oguru, Efanga and the local residents whose interests MD seeks to protect lived and/or worked in the vicinity of the SPDC pipeline.
torts of nuisanceand the
trespass to chatteland on the
Rylands v Fletcherrule. In connection with this, it is firstly noted that it has been decided in 5.30 that in connection with the origin of the leak MD et al. no longer have an interest in these legal concepts, and that in the relevant connection here (of Response) the starting point for the assessment therefore must be that the oil is on the SPDC’s right of way after seeping out of the hole in the pipeline. Against this background, it is subsequently noted that:
Rylands v Fletchercan also not help MD et al. since (i) although it could be said that the oil that ended up on the SPDC’s right of way due to the leak subsequently flowed onto the adjacent grounds from that right of way – because it was not immediately contained – it cannot be said that the SPDC placed that leaked oil on the right of way ‘
for his own purposes’(see legal ground 3.21), meaning that this application condition of the rule has not been met.
The Tort of Negligence in Nigeria’ by Jill Cottrell:
The most important legislative change, relating toapportionmentof damages in contributory negligence cases, has been adopted in all parts of Nigeria’ (underlining by the Court),
internal corrosion seems to be a major problem’ (p. 18, point 5). The risk of a future leak occurring in the Oruma pipeline as a result of corrosion in the pipe is therefore not negligible. According to Shell (point 29 DoA/SoA-cross/2), the percentage of leaks due to sabotage rose to 75% in the 2006-2010 period (compared to 55% before that period, see legal ground 6.18). In the current unsafe situation the risk of sabotage must all the more so be considered as significant. In the past decade, multiple leaks occurred specifically in the Oruma pipeline due to sabotage (see legal ground 5.34). In short, it is fairly likely for a new leak to occur in the Oruma pipeline.
to prevent illegal tapping’ (see the last phrase of question 4 on p. 2 of Exhibit Q.75) and with which sabotage attempts can only be stymied very occasionally, as a lucky break, and which are wholly unsuitable for discovering leaks caused by corrosion.
justice can be adequately done.
Update on Security Operating Levels (SOL) and Security Single Point Approval (SSPA) – Niger Deltaof the SPDC of 8 May 2019 (Exhibit 69) the following report was published, in which Bayelsa State and Oruma are not mentioned:
BLACK, activities that require travel can still be undertaken, under certain conditions and c) travel is permitted under the lower security operating level, SOL
RED, for the rest of the Rivers Delta (including Bayelsa State) provided approval (SSPA) has been obtained. Despite the deteriorated security situation, it remained possible for SPDC employees to carry out work activities – like MD et al. have put forward in point 12 DC-MD/2. This is in line with the code orange that was issued for Bayelsa State, according to which necessary travel was still permitted, and it is also in line with the fact that there had been an unsafe situation in Ogoniland, Rivers State, since 1993, while the SPDC continued to carry out work activities related to the main pipelines running through that area (points 130 and 381 DoA/SoA-cross/2, see also points 157 and 158 SoA/2). According to Shell, this continued even until early 2018 at the village of Goi, Ogoniland (point 106 DoA/SoA-cross/2), although the security situation there had deteriorated too much for a physical inspection by the experts (point 133 DoA/SoA-cross/2). Installing an LDS falls under, or can be equated with, ‘important maintenance’ – of which Shell considers the 2015 ILI run but not the expert examination on site to form part – which in Shell’s view should also be carried out in a highly threatening situation (point 381 DoA/SoA-cross/2). Insofar as Shell’s defence, as stated in 6.41, is to argue that carrying out LDS work on the Oruma pipeline is irresponsible or even impossible, this defence is disregarded as being insufficiently substantiated, meaning that the Court is unable to assess the rebutting evidence as offered in, inter alia, point 936 DoA/SoA-cross/2.
minutes to hours, without physical access being required (see legal ground 6.14). This order pertains to both the Oruma II pipeline, which currently acts as the main pipeline, and the Oruma I pipeline, which as a spare pipeline should be able to take over the function of the main pipeline at any time.
REDsituation in Bayelsa State, the SPDC will be granted the generous term of one year to accomplish this. Since the SPDC has not argued in the alternative for mitigating or capping the penalties claimed, it must be assumed that there is no reason for doing so.
7.The claims against the Shell parent companies in respect of Response
[o]ver the longer term Nigeria will continue to be an extremely important part of our portfolio (...)’ (point 641 SoA/2). On the other hand, Nigeria is also a source of constant concern for Shell. In legal ground 6.18, the large number of Shell leaks per annum in Nigeria was discussed. MD et al. have asserted without contest that in the period 2002-2007, the Nigerian Shell company (SPDC) was responsible for 33% of the total amount of the oil leaked by the Shell group. In the 2005
Business Assurance Letter, [managing director 2] , one of Shell’s Managing Directors at the time, wrote the following to the Shell group’s then CEO, [CEO] : ‘
The Nigerian Delta security and reputation issues continue to be very challenging’ (note 615 to point 652 SoA/2, see also point 889 DoA/SoA-cross/2), whereby ‘
challenging’ was apparently used as the well-known management euphemism for ‘problematic’ or ‘unpleasant’. In view of the considerations in legal grounds 6.37, 6.38 and 6.48, the current situation in Nigeria has certainly not become less worrisome for Shell. Under these circumstances, there are sufficient reasons to believe that the Shell leadership was and still is fairly intensively involved – directly and indirectly – with the SPDC. From the passage in the ruling of the UK Supreme Court, deemed normative by this Court in legal ground 3.29 in the case of
Vedanta v Lungowethat ‘
[e]verything depends on theextentto which, and the way in which, the parent availed itself of the opportunity to take over, intervene in, control, supervise or advise the management of therelevantoperations (…) of the subsidiary’(underlining added by the Court), it is apparent that the question whether or not the parent is liable does not necessarily revolve around whether the parent is involved in the subsidiary in general, but – as Shell has argued (in, inter alia, points 91(c), 104 and 116 WS/2-S) – that it is important whether or not that involvement encompassed the actions of the subsidiary on which the parent liability is based. In this case, it is the SPDC’s omission to apply an LDS or adequate LDS. Parent liability is also contingent on the requirement that the parent knows or should know about the subsidiary’s actions; the so-called knowledge requirement in legal ground 3.30.
‘(are) implemented by the various Shell companies (...)’. Checks on compliance with the group policy takes place at the group level (by RDS) by means of carrying out audits, inter alia.
business, and the CMD’s management came ‘down’ based on that information (point 554 SoA/2), while concrete tasks in the area of, for instance, maintenance and HSE, were relayed in the annual business plans with associated budgets, which the parent company/companies had to approve and the operating companies had to state in
Assurance Lettershow they complied with the group’s security and HSE policy (points 578-585 SoA/2 and points 75 and 139 M-Exh).
Executive Committee, including [managing director 2] , is also determined by the number and volume of
operational spills. According to MD et al., this shows that RDS exerts influence over it. The Court assumes, with Shell, which does not contest the existence of this bonus policy, that the number and volume of
operational spillshas only been included in determining the bonus amounts since 2010.
operational spillson an annual basis across the entire Shell group. However, this does not alter the fact – unlike Shell seems to want to imply – that the focus would have been on specifically Nigeria considering the fact the Nigerian Shell operating company SPDC is ‘responsible’ for a very large share of the total volume of oil leaked by the Shell group, in the 2002-2007 period no less than 33% (see legal ground 7.1.b).
operational spillsis determined, in part and to a considerable extent, by the presence or absence of an LDS in leaks that cannot be verified or whose verification is delayed by access issues. In these situations, an LDS is able to verify the leak within hours, after which the oil supply can be shut down, while without an LDS, this process can take up to three days, such as was the case with the 2005 leak at Oruma. In Nigeria, access refusal is a common problem (see legal ground 6.6), which the Shell leadership is sure to know, not only because of the fact mentioned in legal ground 7.16, but also because:
res ipsa loquitur) that the members of the
Executive Committeeresponsible for Nigeria will also acknowledge in their functional or regional management of the SPDC – due to the not so insignificant influence it may have on their bonus amounts – whether or not the pipelines in Nigeria (including the Oruma pipeline), should be fitted with an LDS, for which they will also base their final answer on other factors and a cost-benefit analysis. RDS’ bonus policy since 2010 will therefore have inspired the members of the
Executive Committeeto fervently involve themselves in the way the SPDC handles the LDS issue. This is also in line with the framework of DEP 31.40.60, presented in legal ground 7.11, and can also be viewed as a concrete specification of the framework, and also as confirmation of the observation therein that the LDS issue affects the group interest.
Okpabi v RDS, referred to in legal ground 3.28. This statement contains the following passage (see also point 70 WS/2-MD), in which (
I), (
II) and (
III) have been added by the Court to distinguish three separate parts:
was an unreliable employee and a bad leaver’, points 12 through to 19). In general, such arguments are of themselves not very persuasive. [witness 2] then explained in point 21 the general position of [witness 1] :
[witness 1] seems to suggest (…) that there is a (…) security function that sits outside of SPDC (…) which exercises complete control over security matters at SPDC. This is not my experience at all’. Point 26 of [witness 2] ’s statements is as follows:
It is of course correct that we keep relevant colleagues within Business and Functional lines abreast of pertinent information, where it is appropriate to do so. For example, we will copy James Hall on email reporting serious security incidents. However, this does not mean, for example, that James Hall or anyone else can seize complete control of security operations at SPDC. That suggestion is simply false’.
meetings, workshops and discussion groupsreferred to by [witness 1] in part
(I)of her statements were, apparently, no bodies where decision-making took place; [witness 1] stated that ‘
during these events’ ‘
various initiatives’ were discussed, and [witness 2] did not argue that this (also) involved decision-making. [witness 2] ’s remark that [witness 1] was ‘
removed from decision making processes at SPDC’and his remarks in point 21, which are elaborations of this point, can therefore not be viewed as a contention of part
(I)of [witness 1] ’s statement. Nothing else in [witness 2] ’s statements proves that the statement of [witness 1] – note: based on personal observation – about the
meetings, workhops and discussionsand all that transpired there, was incorrect. Based on part
(I)of [witness 1] ’s statement, the Court deems it proven that between the SPDC and the representatives of ‘
The Hague’ (apparently RDS, see legal ground 1.b) discussions took place about the introduction of an LDS. This would not have concerned just an exchange of information on an equal basis. That which [witness 1] has stated in part
(II)– namely, that the fairly expensive initiatives were not implemented and that the reason must have been that RDS did not approve them – is also based on personal observation. As a participant to the
meetingsit must be assumed that she knows the overall price of the measures that were discussed, and knowing that the more expensive projects require approval from ‘upstairs’ is not restricted to persons with a special (more than ‘
junior’) position, to which group [witness 1] , according to [witness 2] , does not belong. An approval system for significant expenditure is not the same as the ‘
complete control’ of which [witness 2] speaks. Part
(II)of [witness 1] ’s statement has also not been refuted convincingly by [witness 2] . All in all, there is no reason to doubt the accuracy of this part of the statement, from which also becomes apparent, in addition to part
(I)of [witness 1] ’s statement, that RDS was involved in the question of installing or not installing an LDS in Nigeria. [witness 2] places great emphasis on the lack of specifically ‘
complete control’, which suggests that there was or could have been a less far-reaching type of involvement, such as influence or concern. To that extent, his statement can be interpreted as confirmation of [witness 1] ’s statement. Incidentally, in light of the words used by [witness 1] ‘
I (…) infer’ part
(III)of her statement cannot be assumed to be true in these proceedings.
I) and (
II). After all, Shell does not address these specific parts of the statement, either directly or indirectly.
proximitybetween RDS and the ‘Oruma inhabitants’, which the Court deduces from the consideration in the ‘
Vedanta v Lungowe’ ruling that ‘
the result would surely have been the same if the dust had escaped to neighbouring land where third parties, worked, lived or enjoyed recreation’. In this ruling, the decision in the
Chandler v Capecase, that the parent was liable to the subsidiary’s employees, who had been exposed to asbestos by the subsidiary, was applied to
third parties, with which the ‘Oruma inhabitants’ can be compared. Under the circumstances outlined here, it is
fair, just and reasonableto assume a
duty of careof RDS to ensure that an LDS is installed on the Oruma pipeline. Seeing as RDS has not fulfilled this
duty of care, this also constitutes an unlawful situation on her part. Since the SPDC has remained unwilling for a very long time to proceed to install an LDS on the Oruma pipeline, even in spite of the increased need for it, it is necessary, so that
justice can be adequately done, to also impose an order on RDS, with which it can be ensured as far as possible that an LDS will be installed on the Oruma pipeline at long last.
Vedanta v Lungoweruling of the UK Supreme Court a rule of English company rule was given, namely that ‘
[d]irect or indirect ownership by one company of all or a majority of the shares of another company (which is the irreducible essence of a parent/subsidiary relationship) may enable the parent to take control of the management of the operations of the business (…)’,see legal ground 3.29.
8.The claims in respect of Decontamination
restitutio in integrumapplies as the main rule of damages, as MD et al. have asserted in point 383 R, what comes to mind is that pursuant to the damages that are payable due to the award of claim I alone, and possibly also claim III.a-a, in respect of Origin, a full decontamination of the pollution caused by the leak must be carried out, or at least that an amount must be paid to cover this full decontamination. The same thought could arise in response to the award of claims I and III.a-a in respect of Response/LDS. This also brings up the question which interest MD et al. would still have in an assessment of the claims in respect of Decontamination based on a breach of the duty of care, as referred to in 8.1, an issue which was also raised by MD et al. in point 114 WS-MD. Whether or not Nigerian compensation law indeed assumes
restitutio in integrum, what the consequences of this are and whether or not the above-formulated thoughts are correct, must all be determined in the follow-up proceedings for the determination of damages, so that the Court cannot state at this time that the interest of MD et al. in an assessment of the claims in respect of Decontamination is lost due to the award of claims I and III.a-a. In this context, it may also be relevant that claims I and III.a-a in respect of Decontamination are based on common law, while claims I and III.a-a in respect of Origin were awarded based on the OPA (cf. also legal ground 6.31). The latter claims have furthermore been deemed not-allowable against the Shell parent/parents, so that the claims in respect of Decontamination against the parent/parents are not directly or indirectly affected by the issues discussed here.
Oil Spill Contingency Plan, see under 2.0 on p. 145 – the following is stated (p. 148, 150 and 152):
management and remediation of contaminated land’. Under 8.0, p. 278, it says: ‘
Intervention and Target Values’. The following is stated there, inter alia (on p. 278 and 279):
mineral oil’ (in short: oil) of ‘
soil/sediment’ at 5,000 mg/kg and the target value at 50 mg/kg. For ‘
groundwater’ these values are established at 600 and 50 µg/l, respectively.
shall take prompt (…) steps to contain, remove and dispose of the spill’ is so specific that it may serve to clarify a duty of care, but the recommendation in the same sentence that he ‘
shall take adequate steps (…)’ is too vague. After all, it is not clear in and of itself what
adequatemeans, unlike the word ‘
prompt’, which indicates that (first) steps must be taken to contain and remove the leaked oil directly, without delay. Article 2.11.3 of Part VIII B, which in the preamble mentions ‘
attempt to achieve’, is by its nature not suitable as a basis for a civil law obligation which can be enforced.
prompt’ steps must be taken ‘
to remove and dispose of the spill’. For an explanation of this, they have referred to their arguments on the theme Response in point 380 SoA/2, inter alia. In that context, the actions of Shell in the period up to 9 July 2005, when the oil was being contained, have already been assessed. Regarding the period between 9 July 2005 and the date on which the decontamination commenced, 18 August 2005, Shell took the standpoint in the first instance, namely that up until 18 August 2005 access was being refused (point 87 SoD-a and point 57 SoD-b, see also point 97 DoA/SoA-cross/2). MD et al. have not contested this. In point 487 SoA/2, MD et al. have put forward that about one year elapsed between the leak on 26 June 2005 and the decontamination, but they have failed to specify that, let alone why the decontamination – started in August 2005 and concluded in June 2006 – could and should have been carried out quicker. Taking all this into account, no breach of a duty of care on the part of the SPDC can be assumed in respect of the temporal aspects.
mineral oils(
Total Petroleum Hydrocarbon, abbreviated as TPH) and
metals– to remain below intervention values. The goal is to restore the soil to its original state, and in their view the set target values entail a best-efforts obligation for the operator to organize the decontamination process in a way that those target values are met as far as possible (points 387-389 SoA/2). MD et al. emphasize that the intervention values are not the goal of decontamination and that the EGASPIN standard entails that the soil is restored to its original state as far as possible, and that in sensitive areas, such as mangrove areas, the contamination is removed completely (points 391 and 433 SoA/2).
ir.Th. Edelman, wrote the following on p. 9 of his report of 5 September 2020, submitted as Exhibit Q.72:
monitoring’ and from the last three paragraphs on p. 13 that the condition in 5.2 refers to the situation of the possible presence of residual contamination over the intervention value; if this possibility is not excluded, absence of the need for monitoring is not apparent. In this light, the passages from the Edelman report cited cannot be interpreted other than that the decontamination goal is achieved when the intervention values are not exceeded. Shell rightfully pointed this out in points 50-52 WS/2.
United Nations Environment Programme(UNEP) from July 2011 as Exhibit Q.32. On p. 4 there is a bar chart with ‘
soil samples’, which shows that only sample 23 exceeds the ‘
EGASPIN intervention value’ of 5000 TPH, and that several other samples have a value of between 50 and 5000 TPH. Below the bar chart, on the same page, there is a diagram of ‘
soil samples depth’, where only at sample 23 it states: ‘
Exceeding EGASPIN’, and at all other samples: ‘
Not exceeding EGASPIN’. This also clearly shows that the UNEP assumes that the EGASPIN standard is only exceeded when the intervention values are exceeded.
the current intervention levels (…) are inadequate’ (p. 41) does not carry significant weight – unlike MD et al. believe (point 439 SoA/2). This remark forms part of ‘
recommendations’ for the future (see the caption of 4.2 on p. 41 and point 441 SoA/2) and essentially confirms the application of the ‘
current intervention levels’. The IUCN’s recommendation was also not followed by Edelman in his 2020 report.
to restore as much as possible the original state of any impacted environment’. This description is too vague for this purpose – what does ‘
as much as possible’ mean exactly? – which is underlined by the reference made in that article to ‘
part VIII F’ for the elaboration of this general obligation. The elaboration in Part VIII F entails, as has been established above, that the intervention value must be taken into account.
mineral oil’) exceeding the intervention value was found at
Study Station ‘Oruma 5’, while a sample with a high value was found at
Study Station ‘Oruma 2’. The district court considered in 4.58 of the judgment that it was insufficiently argued and made evident that these two high measuring results were attributable to the oil leak of June 2005. In legal ground 4.60, the district court ruled, in part based on this consideration, that the alleged insufficient decontamination was not established. MD et al. did not submit grounds for appeal against the considerations in 4.58, so that on appeal it must be assumed that the two high values were not caused by the 2005 leak. Nor have MD et al. argued on appeal that the district court’s consideration that the high values were not due to the 2005 leak could not/cannot support its opinion that the decontamination was not insufficient, so that on appeal it must therefore also be assumed that a result exceeding the intervention value, not attributable to the 2005 leak, cannot lead to an award of any claim of MD et al. Incidentally, this also follows from legal ground 3.4 of this ruling. In short, based on the Bryjark report, it cannot be established that a relevant excess over the intervention value occurred. MD et al. have argued, sufficiently substantiated, on other grounds than the report that the intervention value for mineral oil has been exceeded.
from report [17]’ it becomes apparent that there still are high levels of lead and mercury, and where it is also noted that report [17] pertains to Ikot Ada Udo, as is apparent from Chapter 8 of a previous report by Edelman, submitted as Exhibit Q.30. Considering this state of affairs, it cannot be assumed that heavy metals remained present in the soil after the Oruma decontamination.
[b]ut even if the RENA method were internationally accepted, Shell could not have fulfilled its duty of care by using this method, if the results are unsatisfactory after all’. Superfluously, the Court adds here that the criticism of MD et al. of the application of the RENA method in this case is in particular based on the – contested (point 724 DoA/2) – argument that, since it took a while before this method was applied, it is ‘likely’/’probable’ (points 421 and 429 SoA/2) that the oil had dropped down to below the 30 centimetres of excavated soil, but that, considering the words ‘likely’ and ‘probable’ as used by MD et al., it has not been specifically argued, let alone proven, that this actually happened. At any rate, it is has not been proven that the normative intervention values were exceeded.
can exert negative impact’, it fails to state how big this potential impact is. In the following passages of the report there are further clues that the significance of that impact must be regarded in relation to, specifically, surface water and fish:
(…) there has been a significant decrease in the hydrocarbon concentration especially in the surface water based on the relatively dynamic nature of the water system in the area(p. 5);
Previous studies have shown that oil trapped in soils and sediments persists much longer and is likely to cause more environmental problems than oil in water(p. 37);
Adult fish are able to avoid oil-tainted water masses, because they can perceive the presence of oil in very low concentrations. In the event of an oil spill, fish may be exposed to concentrations of oil in water that may be too low to cause death (…)(p. 37).
reduced life in (...) the ponds’. In light of all this and of the considerations in 8.25, the assertion of MD et al. (in points 413, 416, 495 SoA/2) that the ponds were still so severely contaminated after the decontamination at issue here that no fish could live or be farmed in the ponds, lacks sufficient substantiation. For this contested assertion – in support of which the Bryjark report does not provide evidence on account of the reasons stated above and for which no concrete evidence can be found elsewhere in the file – no specified evidence by witnesses was tendered, so that it has at least remains unproven. The mere fact that after the decontamination process, a level of TPH was found in the surface water which could have a negative impact on the environment, but the extent of which is unknown – and which therefore could also be absent or minor – does not justify the conclusion that the SPDC breached a duty of care when purifying the surface water.
in fine). Although it would have been logical for MD et al. to do so, in light of the substantiated defence of Shell in point 724 DoA/SoA-cross/2 that it is highly unlikely that the contamination penetrated beyond the uppermost 30 centimetres of soil, they failed to tender evidence for this course of events. A breach of a duty of care on the part of the SPDC can also not be established as regards the groundwater.
Rylands v Fletcherrule (point 807 SoA/2). They believe that rule applies since a) the soil excavated during the decontamination process was placed on clean soil, which in turn became contaminated by the oil leaking from the excavated, contaminated soil and b) the SPDC dug waste pits in which it dumped oil waste, from which location the oil, seeing as the waste pits were not protected against this, leaked into the underlying soil. However, the Court fails to see that – as expressed by Shell in point 745 DoA/SoA-cross/2 – this caused a contamination which would not have occurred without the excavation of the soil and the dumping of it in the waste pits. If the contaminated soil had not been excavated and the oil waste had not been deposited in a waste pit, the oil would have leaked into the underlying or adjacent soils anyhow. Invoking the strict liability of
Rylands v Fletcheris denied due to the lack of damage. Since the situation referred to here must be deemed to have been terminated, an order to that effect is not relevant.
9.Claims II and III.b: the fundamental right to a clean living environment
African Charter on Human and Peoples’ Rights. MD et al. have based their reliance on the assertion that their living environment is ‘severely’ contaminated (point 737 SoA/2). The Court will start from the common starting point, which is in line with the general opinion about the threshold that must be set in order to be able to designate a violation of fundamental rights for the protection of the environment, see for instance ECtHR, 9 December 1994, A303-C, NJ 1996, 506 (
López Ostra/Spain), in which the requirement of severe environmental pollution was set.
‘Concentrations in excess of the intervention values correspond to serious contamination’) it is confirmed that contamination is deemed severe only when the intervention value is exceeded. Therefore, a violation of the fundamental right to a clean living environment in connection with Decontamination can also not be assumed.
10.Claims III.a-b and IX
11.Concluding considerations
locus standiof MD et al. fail. The contested judgment is quashed and a decision will be made as stated above.
mrs.J.M. van der Klooster, M.Y. Bonneur and S.J. Schaafsma and pronounced in open court at the hearing of 29 January 2021, in the presence of the court clerk,
mr.M.J. Boon.