The Scale and Impact of the Pollution Crisis

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50
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CHAPTER
2

The Scale and Impact of the Pollution Crisis

50
minute read
CHAPTER
2

The Scale and Impact of the Pollution Crisis

That Bayelsa has suffered a pollution catastrophe is beyond question. However, its scale and scope remains inadequately researched.

The Commission has sought to assemble a comprehensive picture of the contours and nature of the crisis engulfing Bayelsa. As well as undertaking an extensive review of the existing literature, the Commission has conducted original scientific field research to capture direct evidence of the effects of oil pollution across the state. All of the LGAs in the state were reviewed and then key areas of LGAs were selected for visits and deep-dive case studies in order to take testimonies from local communities and to assess the nature and scale of pollution.

The Commission interviewed over 500 people, and collected blood samples from 1,600 people to assess the levels of toxicity in their bloodstreams. A key motivation of this endeavour was to ensure that the voices of the communities that have suffered most – voices that have all too often been ignored by decision-makers – are heard. The Commission has developed detailed case studies of select individual pollution incidents to help unravel and illustrate the interplay of causes that are at the root of the problem.

Using this rigorous, multi-faceted approach, the Commission has built a detailed account of the devastation Bayelsa has suffered and the impact on the state’s environment and its people.

The Commission has investigated and reports on the following instances of pollution:

  • Oil spills
  • Gas flaring
  • Effluent waste disposal
  • Divestment
  • The operations and destruction of artisanal refineries

The scale of the oil spills problem

It is difficult to convey or put precise numbers on the magnitude of the disaster that has unfolded over the last 60 years. Findings from different studies vary dramatically, but all of them attest to the extraordinary intensity and sheer variety in the forms of pollution from which Bayelsa has suffered over the last half century. Oil spills, gas flaring, effluent waste disposal, the dumping of drilling waste and mud, and destruction of artisanal refining sites have all had severe impacts on the state. In addition, the proliferation of community conflicts over the distribution of ‘benefits’ associated with oil and gas production activity have all exacerbated and continue to contribute to the entrenched and unacceptably high pollution profile of Bayelsa.

Causes of pollution

Oil spills

An oil spill is oil, discharged accidentally or intentionally, that floats on the surface of water bodies as a discrete mass and is carried by the wind, currents and tides. Oil spills can be partially controlled by chemical dispersion, combustion, mechanical containment and adsorption. They have destructive effects on coastal ecosystems.154

Gas flaring

Crude oil reservoirs in the Niger Delta often contain as much natural gas as crude. From the commencement of oil production during colonial rule, IOCs developed pipeline infrastructure to enable the export of crude oil while they burn the unwanted associated gas through a pipe (also called a flare). Flared associated gas could be used for local energy generation in an area where people do not have access to electricity. However, IOCs and other oil producers do not make adequate investments in associated gas gathering (AGG) infrastructure, which is necessary for converting associated gas for productive use. Instead, IOCs mostly continue to flare associated gas despite the adverse impacts on the natural environment and the health of local inhabitants.155

Effluent waste disposal

Effluent is any liquid waste, other than surface water and domestic sewage that is discharged from premises being used for a business, trade or industrial process. Trade effluent may be waste water contaminated with materials such as:

  • fats, oils and greases
  • chemicals
  • detergents
  • heavy metal rinses
  • solids
  • food wastes 156

Divestment

The process of IOCs selling off business interests in Nigeria, often to local companies.

The operations and destruction of artisanal refineries

Artisanal oil refining is the small-scale crude oil processing or subsistent distillation of petroleum that is often outside the boundaries of the state law.157

Oil spills

A page with seven charts and infographics.   Image 1: NOSDRA recorded oil spill incidents in Nigeria and Baylesa from 2006 to 2020. Nigeria has 12,251 spills and Bayelsa had 3,508 oil spills. 25% of oil spills in Nigeria were in Bayelsa.   Image 2: 109,940 barrels of oil were spilled in Bayelsa from 2006 to 2020. 88% of spills were from 5 IOC facilities.   Image 3: There are 234 oil spills in Bayelsa per year. Most spills were in Southern Ijaw, Yenagoa and Nembe LGAs.   Image 4: The USA is 100 times the size of Bayelsa. It had 137 oil spills in 2018.   Image 5: Europe is 500 times the size of Bayelsa. Europe has 25 oil spills per year.   Image 6: Nigeria’s pipelines are over 565 times more likely to leak than pipelines in Europe.   Image 7: A line chart of annual pipeline spill incident from 2006 to 2019 in Nigeria, Bayelsa, the EU and Canada. In every year, Nigeria has the most spills. In most years, Bayelsa has more spills than the EU or Canada.

158 159 160 161 162 163 164

The figures are stark. But there is considerable evidence that NOSDRA’s statistics may, if anything, understate the number of spills. Material differences have been discovered between the number of spills recorded by NOSDRA and those recognised by the IOCs in their published data.

More strikingly, large discrepancies exist between NOSDRA’s spill data and data released by NNPC itself. For the period 2005- 2018, NNPC’s statistical report identified over 35,670 incidents across Nigeria as a whole, indicating an incident level roughly three times higher than that suggested by NOSDRA.165 If this is correct and the spill distribution were to be extrapolated from the NOSDRA data, this would suggest that Bayelsa has suffered a spill every twelve hours over the course of 14 years.166

An infographic showing that Bayelsa experienced an oil spill every 12 hours for 14 years.

An infographic showing that Bayelsa experienced an oil spill every 12 hours for 14 years.

Even bigger question marks remain over NOSDRA’s assessment of the volumes spilled. Since 2006, the agency states that just over 697,000 barrels have been spilled across Nigeria in its entirety, with 522,000 of these in the Niger Delta.167 Although experts have identified some reporting inconsistencies, the NOSDRA online database indicates that only 109,200 barrels were spilled in Bayelsa between the inception of the agency in 2006 and October 2019. These figures are at odds with those released by NNPC. The national oil company, which is responsible for the regulation and monitoring of overall oil output, states that 33.7 million barrels of ‘petroleum products’ (including liquefied petroleum gas (LPG) and other outputs) were lost between 2005 and 2018, with almost 5 million barrels of crude being unaccounted for between 2013 and 2018 alone.168 The former DPR, of which NNPC was a part, had previously published research estimating that a further 2.4 million barrels were spilled in the Niger Delta between 1976 and 1996.169 The United Nations Development Programme cited similar figures, finding in excess of 3 million barrels of spillage between 1976 and 2001.170 According to a recent report, the DPR had also developed estimates of recent spill volumes that in 2018 were as much as three times higher than NOSDRA’s.171

Part of the reason for these significant divergences may be found in the dysfunctional NOSDRA process. Evidence from multiple independent sources, as well as significant testimony from numerous witnesses at all levels, suggest that the JIV process, which provides the basis for NOSDRA’s assessment of the number and impact of spills, is fundamentally compromised by the outsized role that IOCs play in the process.

Data released by NOSDRA confirms that all too often, JIV reports are often highly incomplete, fundamentally undermining the accuracy of the agency’s figures. Of a sample of over 6,000 JIV reports filed between January 2010 and August 2015, 82 percent included no estimate of the spill area, 71 percent had no description of impact, and 33 percent did not include an estimate of the quantity spilled.172

Even where reports are completed, distortions in the way the JIV process is run render the figures produced deeply unreliable. The Commission’s own findings confirm those of an extensive body of independent research that suggests that the administration of the JIV process is subject to capture by the companies it is meant to regulate (the JIV process is further expanded on in Chapter Three).173

This problem is exacerbated by the obsolescent methods used by JITs to assess the scale of spills and the damage they cause. JITs often rely on highly flawed and outdated techniques, no longer used globally, such as estimating spill areas “by sight”. Particularly in cases concerning bodies of flowing water, this can lead to a significant understatement of leak volumes. In one example (outlined in Chapter Three) the combination of these issues led local residents to claim that the volume spilled had been underestimated by a factor of as much as 60.174

Independent research suggests that the amount of oil spilled in Nigeria is, to a significant magnitude, greater than that suggested by NOSDRA. Research published by Amnesty International and the World Wildlife Fund (WWF) in 2009, using the Nigerian Government’s own data, estimated that 9 million barrels had been spilled over the previous 50 years across Nigeria.175 The Woodrow Wilson Centre offered a higher estimate suggesting a level closer to 16 million barrels of oil.176 All of these figures will have risen since these reports were completed.177

Figures printed on a page fail to convey the enormity of these findings. These numbers describe an almost unprecedented level of oil pollution. The collated data suggests that every single year for the past 50 years. Nigeria suffered the equivalent of a major oil spill roughly on the scale of the Exxon Valdez disaster, an episode that devastated over a thousand kilometres of the Alaskan coastline and became one of the defining pollution incidents in the history of the oil industry.178

An infographic comparing the Alaska Exxon Valdez oil spill to oil spills in Bayelsa. In Alaska, 11 million gallons were spilled. In Bayelsa, between 110 to 165 million gallons were spilled.

Southern Ijaw LGA Town Hall Meeting by BSOEC

“  ”

In 2004, October 13, a spill occurred in my place. We call it Asitowat spillage, from high-pressure Agip pipeline, we wrote to Agip and we were not compensated. The community went to court, at the end, they came and paid a pittance to Gbarain and abandoned our community. There was no clean-up for nine months, and aquatic life was destroyed. Not even relief was provided and no compensation paid. There is another spillage right now in Azagbene not one kilometre to Gbaratoru and Gbanraun, which is the boundary between Ekeremor and Southern Ijaw LGA. So far, 14 children have died because of this spill. This is how we have been treated. There are no hospitals, the children just fall down and died. We are drinking the same polluted water.

Resident
Ukparatubu Community

This overwhelming tide of oil contamination has, as a result, turned the Niger Delta into one of the most polluted places on Earth.179

A map showing pipeline concentration in Bayelsa and Rivers.   There is a dense network of operating pipelines throughout both states. There is new proposed and under construction pipeline in Northern Bayelsa and Rivers.

180

Patterns of oil spills in Bayelsa

Bayelsa State has borne a significant proportion of the Niger Delta’s oil and gas-related pollution. As outlined above, 26 percent of spill incidents and more than 15.6 percent of spill volumes cited by NOSDRA have occurred in Bayelsa between January 2006 and December 2020. Applying these as ratios to the widely recognised independent assessments of how much oil has been spilled in Nigeria suggests that Bayelsa has conservatively suffered 2-3.5 million barrels of oil spilled over the last 60 years.181 If the NNPC figures are correct, the numbers could be higher still. According to official figures, the number of spills in Bayelsa have fluctuated significantly in the last 15 years:

A chart showing annual oil spills by year in Bayelsa between 2006 and 2019, according to NOSDRA.   In 2006 there were fewer than 50 spills, increasing in 2007 to over 100. There is an increase each year until a peak in 2014 of 700 spills. There is a decline over the following years until 2018 when there were fewer than 100 spills, followed by an increase in 2019 to more than 100.

182

While every single LGA in Bayelsa has suffered oil contamination, the problem has been especially concentrated in just a few parts of the state. According to official estimates, the Southern Ijaw, Brass and Nembe LGAs have together accounted for 60 percent of all spills the state has experienced.183

A photograph of a child standing near a river. In the foreground are large containers for oil.

A photograph of two people on paddling a boat down a river.

A photograph of the landscape of Bayelsa taken from high in the air. The ground is a mix of open fields and wooded areas, with many rivers and small creeks throughout.
Photo by Ed Kashi

Share of oil spills by LGA, 2006-2019, Bayelsa

A pie chart of showing oil spills in Bayelsa, by Local Government Area 2006-2019. 57.2% of oil spills were in southern Ijaw, 15.3% were in Brass, 10.1% were in Nembe, 7.5% were in Ekeremore, 7.3% were in Yenegoa and 2.3% 2343 in Ogbia

184

Even after taking into account that the figures are likely to be underestimates, the official statistics paint a sombre picture. And behind each number lies a story. The Commission has heard from hundreds of people living in affected communities and conducted over a dozen detailed deep dives to gather information in affected communities. There has been particular focus on Southern Ijaw, Yenagoa and Nembe LGAs - due to their exposure to oil spills - with on-the-ground teams undertaking in-depth research to understand what occurred and what impact pollution has had in individual cases. Elements of their testimony are outlined below:

“  ”

June 2019 spill was an eyesore, as it killed marine life, with fishes dying from the spill.

Community Leader
Nembe185

“  ”

In 2012 there was also a gas explosion that affected every life of Koluoma, the explosion was so massive. As we speak, nothing has been done to ameliorate the plight of the people.

Community Leader
Southern Ijaw186

Testimonies paint a consistent picture. Villagers in communities across the state tell of pipelines suffering numerous leaks, of IOCs all too often denying the scale of the leaks, or, controlling the JIV process in an effort to minimise their liability for compensation.

A photograph of a riverbank with oil-contaminated water.

Pollution in Bayelsa: More than oil spills

Pollution in Bayelsa is not limited to oil spills alone. Other activities including effluent waste disposal in the Brass Canal, dumping of drilling mud, artisanal refining, and gas flaring have also added to the toxic mix of contamination.

Gas flaring

As well as being an ongoing source of pollution in Bayelsa and elsewhere in Nigeria, gas flaring is a major contributor to regional and global climate change. Although many other jurisdictions around the world have outlawed the practice, Nigeria remains one of the main locations of gas flaring by the international oil industry.

Routine gas flaring disposes of associated gas through open burning during oil production in locations where oil companies decide not to build the infrastructure to process, use, market, or re-inject into the reservoir. In Bayelsa, and the Niger Delta more broadly, large flares burning from towers and land surface areas have been prevalent since the inception of the Nigerian oil industry in the 1950s. Flaring has been, and remains, the main means of disposing of waste gas produced by oil extraction in the country.

Flaring is an enormous waste of a valuable natural resource that should either be used for productive purposes, such as generating power, or conserved.187

Although gas flaring is a necessary part of the petroleum producing process, statistics from various countries show that no country flares as much gas as a percentage of their total gas as Nigeria.188 According to World Bank data (2021), Nigeria is in the world’s top ten gas flarers in terms of volume and flaring intensity.189 Libya for instance flares about 21% of its natural gas, while Saudi Arabia, Canada and Algeria flare 20%, 8% and 5% respectively, conversely Nigeria flares up to 90% of its associated gases.190

A chart showing the percentage of natural gas flared by county. Nigeria flares 90%, Libya flares 21%, Saudi Arabia flares 20%, Canada flares 8% an Algeria flares 5%.

According to the World Bank’s Global Gas Flaring Reduction Partnership (GGFR191), in 2021, Nigeria was the seventh largest emitter of gas by flare volumes. 6.6 billion cubic metres (bcm) were flared representing 17.67 million tons of CO2 emissions at an estimated cost of US $760.58 million.192

The top 10 largest flaring countries in 2021 – Russia, Iraq, Iran, the United States, Venezuela, Algeria, Nigeria, Mexico, Libya, and China – accounted for 75 percent of all gas flared while the top seven (a group that included Nigeria).

According to GGFR data, the 20 Nigerian fields with the largest flaring volumes averaged over 150 million cubic metres (mcm) annually per field while the number of fields discharging gas between 2012 and 2021 increased from 168 to 180. While the volume of gas flared dropped by 30 percent from 9.6 bcm in 2012 to 6.6 bcm in 2021, gas flaring intensity – i.e. the volume of flared gas (cubic metres) per barrel of output produced – increased from 10.73 in 2012 to 11.75 in 2021. This implies an almost 10 percent increase in flaring intensity between 2012 and 2021. One study cites flaring at 139 of 177 oil field sites in Nigeria highlighting that the majority of sites flare gas.193

Nigeria’s total gas consumption in 2019 was 15 bcm which means the amount estimated to have been flared would have met nearly half of Nigeria’s needs.

Statistics on flaring vary. While state level data is available from NOSDRA, there are some inconsistencies with the World Bank’s Global Gas Flaring Reduction Partnership (GGFR) data and with the state government’s own data. A study citing Bayelsa State Government figures finds 17 onshore sites flaring an average of 13.7 mcm of gas per day.194 GGFR data finds 14 major on and offshore flaring sites that account for 39.5 Mscf* in 2021 (roughly one sixth of the country’s flare volume) while NOSDRA estimates 20.8 Mscf flare volume from a total of 23 onshore and five offshore flare sites.195 Despite the varying statistics, on a per capita basis, Bayelsa’s flaring rates are the highest in the region.

At LGA level, Bayelsa flaring figures highlight that the LGAs most surrounded by water and thus not accessible by road, only by boat, are the most affected by gas flaring. These are Nembe, Ekeremor and Southern Ijaw; all of which have a high number of flow stations and oil operations.

These LGAs will need more resources to tackle flaring and the impact of it.

While federal fines for flaring have been on the legislative books in Nigeria for decades, these penalties have been insufficient to deter the practice. The oil industry cites the Nigerian government’s inadequate regulation in this area as a key factor in flaring’s persistence, but market factors also play a prominent role: building infrastructure to process gas for the local market is not profitable enough for the IOCs.

The prevalence of gas flaring in Bayelsa means that local communities are unfairly exposed and bear the environmental and health impacts of this dangerously polluting act. Flaring locations are indiscriminate and flares have even been operated close to schools. Estimates suggest that 2.2 million people across the Niger Delta live within four kilometres of a flaring site.196 330,000 of those people live in Bayelsa.

Gas flaring produces harmful volatile organic compounds (VOCs), polycyclic aromatic hydrocarbons (PAHs), and inorganic contaminants. Other byproducts of flaring include nitrogen, carbon and sulphur oxides (NO2, CO2, CO, SO2), particulate matter, hydrocarbons and ash, photochemical oxidants, and hydrogen sulphide (H2S).197

Several health studies have documented the connection between gas flaring and a range of chronic diseases including bronchial, rheumatic and eye conditions along with hypertension.198

Constant inhalation of sulphur oxide (SO2)causes nose and throat irritation and shortness of breath.199

Prolonged exposure to flared gas has also been associated with cancer and neurological, reproductive and developmental effects. On Commission visits, local residents reported lung and skin damage and deformities in children as impacts too.

Despite all the evidenced health impacts, oil companies have brazenly published photos of Niger Deltans drying cassava or fish from the heat of a flare with the justification that flaring offers a functional benefit to local livelihoods, when in fact livelihoods are being destroyed and lives shortened.

The flares harm and disperse local wildlife and are associated with numerous ecological problems including acid rain. The ‘black soot’ problem evident in Rivers State is a looming issue for Bayelsans.200 When petroleum products are burned carbon is released into the atmosphere, causing soot particles to drop on and stick to houses, clothes and other materials.201 Gas flaring causes contaminant build-up, deteriorating water quality,202 poor agricultural yields and the economic and ecological deterioration of important Deltan food staples, such as cassava, yam, cocoyam, and local fisheries.203 A 2013 study of the pH of rainwater near flare sites indicated that in most cases, the pH levels were below the acceptable WHO minimum, indicating high acidity.204 Given the broader context of ‘energy poverty’ in the Niger Delta, where excessive flaring takes place while local residents lack affordable local cooking fuel, the ongoing burning of waste gas is particularly frustrating and hazardous for the affected population.

A photograph of a gas flare.
Shell gas flaring at the Gbarain/Ubie gas processing plant located in Gbarantoru community, Yenagoa LGA

The impact of gas flaring

IOCs operating in Bayelsa continue to flare gas at an extensive rate with flare sites often situated near residential homes, farmlands, and water sources. In Ogboinbiri and Tebidaba, in Southern Ijaw LGA, Eni (Agip) operates 24-hour gas flaring cycles.205

The Ogboinbiri site is located just 200 metres across the river from the community and Tebidaba’s flare site is separated from the residential area only by a wire mesh fence. In Nembe Creek I, II and III, Oporoma and Gbarain (in Nembe, Southern Ijaw and Yenagoa LGAs, respectively), SPDC continually flares gas except when operational issues arise. In Nembe Creek, the sites are situated around 100 metres from human habitation across a narrow canal. The impact of gas flaring is such that in Nembe Creek, residents describe the flaring effect on their communities as ‘carry over’ during those periods when thick, dark, and misty fumes pollute the local atmosphere for hours to the extent that they force residents to stay indoors to avoid the toxic discharges.

The Gbarain area in Yenagoa LGA is a major gas flaring site. A 2019 study of gas flaring in the communities surrounding the Gbarain Ubie gas processing plant found that, with the exception of carbon monoxide, the concentration of gaseous pollutants in air samples in the region exceeded the standards of Nigeria’s Federal Ministry of the Environment.206 A recent study of Total Suspended Particulate Matter (TSPM) across Yenagoa LGA recorded TSPM concentrations that significantly exceeded WHO and Nigerian federal standards at four sampling sites, with the highest levels of toxicity found at Gbarain Ubie.207 At their highest reading, TSPM concentrations – a cause of respiratory and cardiovascular disorders – surpassed the Nigerian federal standard by a factor of almost 10 during the wet season and 15 during the dry season. 208 In addition, sulphur dioxide concentrations at most study locations exceeded the federal standard during dry periods.209 In all the study area’s locations, VOC concentrations in both wet and dry seasons were in breach of the Federal Ministry of Environment’s standards.210

The Commission’s field work in Bayelsa state captured testimony on the devastating impact of flaring on health in the region:

A photograph of two people standing near a building. In the background is a large gas flare.
Photo by Ed Kashi
Local communities must live with the pollution of gas flaring on their doorstep.

Testimonies from communities affected by gas flaring - BSOEC Hearing

“  ”

I was once the youth leader of this community, but now I am the Chief Security Officer of the community. Really, this gas flaring is suffering us. Our children are affected health-wise and our crops are not doing well anymore. Even with the rain water, we cannot drink it anymore. So we are begging the world, we are begging the Federal Government to come to our aid. Our houses are cracking because of the shaking; we cannot sleep at night. All our windows are shaking, our roofs are shaking.

Male, 41
Gbarain

“  ”

Let the world hear this. The Gbarain people are suffering; Shell is suffering the Gbarain people. Our leaders are not doing anything; we are suffering. So we are begging those in authority, we are dying here.

King B Dakolo
Gbarain Ekpetiama

“  ”

What we are experiencing about this gas flare, the gas flare is killing us silently. Since they started this gas flaring; we no longer live a comfortable life in this community; even my house. I cannot sleep well because of the vibration of this gas flaring. Houses are cracking and even the roofs have been damaged. Even the rain water, we can no longer drink because, when it rains the water would be covered by soot, so dark. So, no one is drinking rain water anymore in this environment. When it rains and you go to the river, the top layer is always black. It is affecting our fishing too. Even our crops; plantain cannot do well again. We are suffering, in fact. The heat is causing so much health issues. We attribute most of the diseases experienced in this community to the gas flaring and; we are not happy about it.

Male resident
Polaku community

NOSDRA Gas Flare Data 2012-2019 Bayelsa State211

A map of Bayelsa and neighbouring states, dotted with the location of gas flares.

Effluent waste displosal: Brass Canal

The Commission heard repeated testimony about the release of polluted water and drilling fluid into waterways. To give one measure of the extent of the problem, the case of the Brass Canal, on Bayelsa’s Atlantic coast, typifies the pollution issues resulting from the unregulated dumping of toxic hydrocarbon waste into the Brass river and onward into the Atlantic. The canal in fact was specifically designed for this purpose. Built by Eni (Agip) in 1973, the Brass Canal is a 3.2 km long waterway designed to discharge produce water, oily sludge and other effluents from Nigeria Agip Oil Company’s (NOAC) Brass terminal. Operated by Eni (Agip) for over 40 years, the terminal is situated on the coast and houses a tank farm for storing crude oil, a skimming unit, office spaces and accommodation. The canal separates the local Brass community from the oil terminal. Pollution of the canal itself and in the canal bank soil and sediment has resulted from the build up of hydrocarbon substances over the last 40 years. The Commission received written and photographic evidence and heard numerous testimonies from Twon-Brass communities and their legal representatives about repeated (often frustrated) attempts to secure justice and fair compensation for decades of environmental damage and systematic destruction of livelihoods and living standards as a result of systematic river pollution.

Immediate action should be taken to address continuing pollution by NAOC-Eni at the Brass Terminal by implementing in full the recommendations of the Inter-Ministerial Ad Hoc Committee Joint Visitation in March 2018 to the Brass Oil Terminal, and evidence submitted to the BSOEC (2019-2020).

Dumping of drilling waste

In September 2020 The Bayelsa State Ministry of Environment noted SPDC dumping untreated drilling waste at the Etelebou-Gbarain dumpsite along Tombia Road in Yenagoa LGA. There is evidence suggesting that this is not the only location affected by this phenomenon, nor is SPDC the only IOC responsible for such indiscriminate disposal of drilling waste. Drilling waste was found to have been deposited illegally at Agbere, in Nembe LGA by a contractor working for Eni (Agip). Although the waste is noted to have been cleared, residents still experience and suffer the negative effects of chemical substances remaining in their ponds, lakes, creeks and other water tributaries.212

A photograph of an excavator on a river bank.
Excavators dredge water to make it deeper and flow better; the mud is then used to pad the river banks.

A photograph of river water with a pronounced sheen of oil.

Pollution from the destruction of illegal artisanal refineries

The Commission uncovered community testimonies about artisanal refining. This is where illegally syphoned crude is refined into consumer fuels for the local market by unemployed youth and traders working in connivance with state security personnel.213 Artisanal refineries contribute to the overall contamination of production sites and the surrounding areas.

The artisanal refineries phenomenon is a product of governance, regulatory and response failures that resulted in the impoverishment of local people and limited access to energy in the Niger Delta and Nigeria generally. Many in Bayelsa and other parts of the Niger Delta are not connected to Nigeria's national electricity grid. Even for those connected, public electricity is notoriously unreliable, and government offices, businesses and affluent families invest in noisy and expensive electricity generators dependent on diesel and petrol. Within the cities and rural communities, low-income families use kerosene for cooking. The absence of an extensive railway network in the country also means that most transportation is by buses, car taxis and motorbikes that run on petrol and diesel. In Bayelsa, many residents travel between towns by motorboats that are expensive to fuel.

Meanwhile, long-term corruption in NNPC's refineries resulted in their collapse and the chronic shortage of consumer fuels. For about two decades, Nigeria has imported most of its consumer fuels due to low domestic refining capacity, and despite millions of dollars expended by the federal government to reactivate NNPC's moribund refineries. However, the fuel importation regime is often unstable, with moments of acute shortage of consumer petroleum fuels, such as during the last quarter of 2022 and in the build-up to general elections in February 2023, crippling whole regions of the country.

National fuel shortages were commonplace nationwide as Nigeria transitioned from military to civilian rule in 1999. With worsening poverty, some youths started scooping crude oil from spill sites, refining it into consumer fuels in the bushes. As the demand for illegally refined fuel increased amidst nationwide fuel shortages, more youths and traders began syphoning crude oil from pipelines for refining in bush camps where they use metal containers as pots to distil crude oil by cooking the product over boiling points to produce petrol, diesel and kerosene. Artisanal refineries supply consumer fuels to communities that would otherwise not have affordable access. Operators of artisanal refineries that spoke to the Commission claim that they supply over 90 percent of the kerosene available for domestic use in the Niger Delta, without which low-income families would be unable to cook their food. Artisanal refiners also contribute substantially to diesel supply, essential to business operations in the region's cities and elsewhere. A respondent narrated to the Commission how Nigerian Agip Oil Company (NAOC) staff in Bayelsa sometimes buy fuel from artisanal refiners to operate company vehicles.

A photograph of a small building surrounded by trees and empty barrels. The building is on fire, with flames fully engulfing the roof and producing large amounts of black smoke.
Naval officers set fire to an artisanal oil refinery camp.

Environmental impacts of artisanal refineries

Leaks occur when people illegally drill into pipelines to syphon crude oil and during the transportation of crude, sometimes on wooden boats (called Cotonou boats) and barges, to refining locations. At the refining sites, crude oil is stored in tanks, drums or open pits lined with plastic or tarpaulin sheets to prevent the product seeping into the ground. However, leakages occur, and the land around such reservoirs is often visibly polluted. Workers in the sites use buckets to scoop crude oil into the refining tanks. Crude oil is also used as cooking fuel to heat the tanks during the distillation process.

Furthermore, artisanal refiners do not have a safe method for managing waste products. There is damage to the local vegetation from cutting trees and fires. The air is polluted with hydrocarbon soot and could impact communities kilometres away.

Members of communities in Bayelsa State generally acknowledge the adverse environmental impacts of artisanal refineries, including the contribution to crude oil pollution. While there were incidences of sabotage of oil pipelines and other installations with the emergence of artisanal refineries, local communities fiercely contested the attribution of most spills to sabotage. All communities visited by the Commission insist that oil companies' attribution of a more significant number of oil spills to sabotage is an attempt to avoid liability, including the payment of compensation to victims of pollution.

A photograph of a man in a uniform puncturing a barrel of oil.
A naval officer punctures a barrel, releasing petroleum into wetlands.

Heavy-handed and environmentally damaging state security responses to artisanal refineries214

The Nigerian government continues to address illegal oil refining principally through Joint Military Task Force (JTF) raids on refining camps, which has not proved an effective long-term strategy. The Niger Delta has remained militarised since the 1990s when the military regimes established Joint Task Forces (JTFs) of soldiers from the army, navy, air force, police and the Nigerian Security and Civil Defence Corps (NCSDC) to pacify community protests and conflicts in Ogoniland and other parts of the Niger Delta. Successive governments have renewed mandates of the JTF to respond to different situations, including artisanal refineries. The security operatives deployed to the Niger Delta lack adequate training and do not seem to have a coherent strategy to deal with artisanal refineries.

The soldiers routinely destroy such facilities in ways that exacerbate environmental pollution, such as setting refining sites, crude oil reservoirs and refined products ablaze. Soldiers operating in Bayelsa State and other parts of the Niger Delta routinely burn Cotonou boats and other vessels laden with crude oil or refined petroleum products right on the creeks. Oil spills also result from such military actions, with fires creating more significant soot pollution than artisanal refining operations.

The JTF's activities have temporarily interrupted some refining operations, using brutal tactics that involve human rights abuses. Military responses deepen the sense of alienation between communities and the state. "Our problem is the JTF," one source in Delta State said, "they set our camps ablaze and kill our children". Community members and operators of artisanal refineries that the Commission spoke with insist that the military's dramatic actions are all a ruse to give the impression of performance during moments of heightened political pressure and to punish operators that do not pay bribes. Beyond attacking the artisanal refining camps and vessels, the military has had little impact on the organised trade in crude oil theft for national, regional and international markets. In 2012, the JTF claimed it carried out 7,585 creek patrols. These claimed to have destroyed 4,349 illegal oil refining camps, captured 133 barges, 1,215 Cotonou boats, 187 tanker trucks, five storage tanks, and 18 seagoing vessels suspected of carrying stolen crude or illegally refined products. Given the ease with which illegal camps can be rebuilt, most camp owners and workers interviewed did not see the JTF's activities as a significant long-term threat to their activities.

The reality is that illegal oil refining is too ingrained within the local economy for violent, ad-hoc military raids to contain it. As recently as 2022 1,800 illegal oil refining sites and sea robbery camps were destroyed and 699 suspects were arrested for complicity in crude oil theft, and pipeline vandalism. Yet at the same time the scale of oil theft grew considerably. In the first half of 2022 an estimated US $7 billion of crude oil was stolen. The Nigerian National Petroleum Corporation (NNPC) admits losses of 470,000 barrels per day but industry experts estimate that the figure could be as high as 600,000 bpd. The loss of livelihoods, lack of opportunities for young people, and limited access to energy services, including the well-known shortage of refined consumer fuels, particularly in riverine communities, all contribute to incentivising the proliferation of artisanal refineries. There is a need for an integrated approach that combines a reformed and informed law and order approach with initiatives that address the underlying causes and drivers of artisanal refineries. Well-planned clampdowns that respect human rights, local norms and the environment could be part of a larger, cross-cutting strategy for combating illegal oil refining. However, without alternative livelihoods, improved service delivery and legal product distribution networks, illegal refiners will find other ways to thrive as camp operators can quickly rebuild their operations in new locations.

Divestment

There are issues surrounding liability and legacy with respect to oil and gas infrastructure, production and exploration and associated related pollution, in the context of divestment, i.e. where IOCs sell off their assets to “indigenous companies” and shift operations to deep offshore areas.

For more than a decade IOCs have been selling off their onshore assets (which tend to be located in places where communities live), to Nigerian companies. In turn they have stepped up their investments offshore in more lucrative and less exposed (to community challenges) deep water extraction sites. Asset sales have tended to take place in secrecy, with limited public oversight with respect to questions of liability for (past and future) pollution damage associated with sold assets, which has been determined contractually between buyer and seller, rather than by regulatory authorities. Changed ownership from international to national companies, has made it more difficult for communities and their representatives in Bayelsa to get their voices heard by Nigerian companies, either through the courts or through protests.

Case study: Pollution and divestment in Nembe

A particularly significant case is that of Nembe, where Shell divested its 30 percent asset share (of OML 29 and the Nembe Creek Trunk Line), for which it had been the operator of a JV with NNPC to Nigerian company Aiteo in 2014/15. This took place four years before the oil mining lease (OML 29) was due to expire in June 2019 (the lease has since been renewed). The case raises questions of responsibility for clean-up and remediation and how liability is shared and/or conferred, when IOCs have “divested” or “decommissioned” yet pollution impacts are ongoing.

Nembe LGA is the site of OML 29, containing 11 oil and gas fields which are Bayelsa’s largest and most productive onshore oil fields. The Nembe Creek Trunkline carries oil from OML 29 to an export terminal in Bonny. Nembe also contains oil fields operated by Eni (Agip). For over 30 years violent conflicts over oil-related goods have pitted different Nembe communities against each other. Relationships with IOCs have been central to these conflicts as has the award of clean-up contracts for oil spills management.

The circumstances in which divestment by Shell of onshore assets took place are non-transparent. DPR records in 2014, which is made up of 2013 data, was already showing Aiteo as the owner of assets. The contract negotiations took place with the Ministry of Petroleum Resources, from which communities from Nembe were absent. There was little to no public discussion about the transfer of liabilities for pollution or compensation for cases pending (related to some of the spills listed below).

  • Between 1985 and 2000 more than 50 cases of oil spills have been recorded and more than 500,000 barrels of crude oil have spilled into the swamps, creeks, rivers, and ocean215
  • 17 spills since 2009216
  • 2019: 1 March - Large spill which resulted in an explosion and 50 people were declared missing. NCTL (operated by Aiteo) shut down
  • 2019: June-July – oil spill at Obama (Agip) flow station
  • 2021: Santa Barbara wellhead blowout

Anecdotal evidence suggests that since Aiteo took over from Shell, the number of spills has increased as have the volumes lost through systemic leakages and theft, with increased associated environmental impacts.

Asset divestment, legacy Issues, challenges

Since 2010, Shell has been implementing a divestment strategy, divesting from its onshore and shallow water assets, in order to concentrate offshore, for commercial reasons.217 Between 2010 – 2015 RDS has earned US $4.8 billion from the sale of its assets.218 Yet divestment does not mean withdrawal, but a shift to deep offshore areas.

Ostensibly divestment is also a strategic decision as a result of threats to the industry. Such threats include the illegal production and sale of oil, greater environmental rights awareness among community groups, and likely increased legal action against IOCs in local and foreign courts for environmental infractions. This heightens fear of incurring heavy costs in remediation of polluted sites and huge financial compensation to communities.219

According to the NGO ERA, the secrecy around the sale of OML29 to Aiteo was deliberately orchestrated to keep communities, who would have wanted to acquire part stakes in the assets themselves, or insist that liabilities of environmental remediation outstanding, out of the picture.

Special purpose vehicles were set up to allow the communities to participate in asset acquisition. Yet all assets in the end were bought and sold in Lagos. The regulators (DPR, NNPC, NOSDRA, Ministry of Environment) appear to have played very little, if any, role in the transactional – contract negotiation stage, with very little discussion about outstanding environmental pollution matters. If these issues had been raised, the scope would have existed for the seller to indemnify the purchaser with respect to issues that may have arisen as a result of damage that was already in place, even where there was no litigation pending.

Nembe Santa Barbara Well 1 Blowout

Oil spills are not only caused by active operations nor are they quickly contained. On 5 November 2021, a blowout of crude oil from the inactive Santa Barbara Well 1 in Nembe Local Government Area (LGA) led to widespread contamination of surrounding land and waterways. The well is owned by Nigerian energy firm Aiteo, which initially blamed the blowout on sabotage prior to a JIV visit and report. The spill was captured in video footage as a high- pressure brown stream of crude oil that was liberally polluting creeks near the site. An initial investigative visit was apparently unable to approach the wellhead due to hydrocarbon fumes that saturated the atmosphere in the area. In the event, Aiteo struggled for over a month to contain the spill and ultimately had to seek the assistance of the US-headquartered specialists, Halliburton Boots and Coots, to seal the well.220

The Nembe incident raises questions about the circumstances surrounding Aiteo’s asset acquisition in the period 2013-2015 and the more recently acquired OML 29 between 2015 and 2019, from former long-term owners SPDC (Shell) who divested their assets to concentrate on offshore development. The secrecy surrounding the acquisition and absence of prior community consultation has been challenged by those currently in litigation against Aiteo (and previously Shell) in the Bayelsa courts. The Nembe Santa Barbara blowout, and the divestment that preceded it, should serve as a test case for how not to conduct asset divestment in the future. Full environmental impact assessments and transparent community consultation should be a standard requirement before any asset divestment.

The Santa Barbara Well also suggests that new legislation should include firm provisions on who bears liability for pre-divestment oil spills. It is arguable that this should not be left to contract, but rather be captured in legislation that clarifies the obligations of all the parties involved when oil companies elect to divest from their assets. There should also be community participation in asset sales and divestment, with transparency over the status of Global Memorandum Of Understandings (GMOUs) signed with the divesting company. Provisions for community participation in asset interest acquisition should be included alongside environmental impact assessments as an integral feature of asset sales protocol. Regulatory bodies such as the Ministry of Environment and NOSDRA should be involved in the contract stage alongside the Ministry of Petroleum Resources.

Nembe responses to asset divestment

For local communities, divestment of oil and gas assets to indigenous oil firms by Shell looks like an attempt by the company to avoid its ecological liabilities.

In 2015 Nembe communities placed a Caveat Emptor or ‘buyer beware’ to ward off would-be buyers of the danger of such business that includes not just assets but also environmental and social liabilities, notably what will happen to the unfulfilled obligations under the GMOUs. Nembe Chiefs Council wrote a letter to the Country Director of Shell at its corporate headquarter office in Port Harcourt regarding divestment of OML 29, requesting the following:

  1. 10 percent equity participation in the divestment of OML 29
  2. Complete the Nembe Gas Turbine for the years of deprivation
  3. Fulfil commitment to SETRACO on the Ogbia- Nembe road under construction
  4. Pay and discharge all outstanding GMOU obligations
  5. Pay all ongoing scholarships (secondary and tertiary)
  6. Diesel supply continues until the completion of Nembe Gas Turbine project. The community should recommend contractors
  7. Turbine engines already in the country should not be disposed or reallocated but handed over to the community
  8. Pay all outstanding obligations on previous pollution and spillages
  9. Clean up and restore the environment, adopting international standards and procedures
  10. Formally, introduce the incoming operator (company) to the community. All outstanding liabilities to be handled by new operators should be formally documented and agreed by the community and the parties concerned
  11. There should be general goodwill payment, i.e ex-gratia.

Determining who bears liability for spills post divestment may depend on the type of divestment that occurs. In effect if Shell divests its assets to another company, then it may still be liable for a cause of action which arose pre-divestment, but may not be liable for a post-divestment cause of action. But this is complicated by the fact that a spill may occur post-divestment but actually be the result of pre-divestment negligence in the laying of a pipeline, or in failure to adopt certain procedures which may have prevented the spill from occurring. In such cases the divester may be called upon to bear responsibility.

Specific recommendations related to the Aiteo asset acquisition from 2013-2015 and the recently acquired OML 29 between 2015 and 2019 should be developed after consultation with those currently in litigation, and, in view of the Santa Barbara Well 1 blow out month-long spill (November - December 2021), measures taken to identify clearly the precise oil spills profile in these cases and what the liabilities are. Nembe could have been a case study for how to conduct asset divestment responsibly with environmental impact assessment requirements as standard before any asset divestment.

There is a lack of clarity in Nigerian law with respect to divestee liability. This has potentially serious negative consequences on the ability of communities to defend their rights to compensation, clean-up and remediation. First, they are less likely to be able to hold the divestee liable in the Nigerian courts for pollution impacts that are the result of negligence prior to sale, or take the new company to court internationally, given its registration as a Nigerian company. The legal frameworks particularly to liability for historical spills need to be assessed.221

The Commission’s impact studies

A toxic legacy: The impact of pollution in Bayelsa State

The Commission has sought not only to identify the environmental, economic and health consequences of pollution, but also to identify irrefutable evidence of their underlying chemical causes. To do this, the Commission has sought, for the first time, to identify the toxic footprint that oil contamination has left on Bayelsa.

The Commission undertook two scientific studies to assess different facets of the pollution crisis.

The first study, the Environmental Impact Study, focused on the environmental impact. Working with Professor Allan Jamieson, an acknowledged leader in the field of forensic analysis, the Commission reviewed analysis of samples taken from 17 sites to test hydrocarbon-related toxin contamination levels in soil, water, air, selected animal species, as well as human blood and tissue.

The second study, the Human Health Impact Study was undertaken by the Commission to assess the impacts of pollution on human health. 1,600 blood samples were taken from volunteers from four LGAs in Bayelsa, with 400 samples from each community.

All sampling and testing for both studies was undertaken according to strict international standards. A detailed description of the methodology is laid out below.

Scientific study methodologies

Environmental Impact Study

The Commission engaged leading forensic scientist Professor Jamieson and Dr Sarah Gomes to critically peer review an environmental impact study commissioned by the Bayelsa State Government in 2019. This study was conducted to identify the effects of hydrocarbon pollution on critical elements of the environment in Bayelsa. Samples were taken from multiple locations across 17 localities in seven LGAs in Bayelsa. The sampling locations were selected from sites based on their ecological features, geographical proximity to a spill site, and their locations within a two kilometre radius of a major oil facility. Soil, groundwater, surface water, sediments and samples of plants and aquatic organisms that often enter the human food chain were collected at multiple sites in each location to assess for contamination. Air samples were also taken. The United States Environmental Protection Agency (USEPA) method was used for the field sample collection.

The results of the testing were then reviewed in depth by Professor Jamieson, who visited Bayelsa accompanied by Dr Sarah Gomes to meet with the research teams, visit some of the laboratories where samples were tested, and to review the data and reference material included in the original report.

A photograph taken close to the ground. The vegetation in the foreground is brown and decaying. A strip of caution tape is strung across the area.
Farmland is frequently ruined by oil contamination, destroying local livelihoods.

The analysis of the samples focused on five groups of contaminants:

1. Polyaromatic Hydrocarbons (PAHs).

PAHs are a group of over 100 organic compounds that occur naturally in crude oil. Their distillates are produced when hydrocarbons are burned. While further work needs to be done on the health effects of PAH exposure, there is general acceptance that they pose a health risk, particularly in relation to cancer. As a consequence, jurisdictions such as the US have set recommended limits for workplace exposure.

2. Total Petroleum Hydrocarbons (TPHs).

These are a family of several hundred chemical compounds that derive from crude oil. The compounds have different effects and exhibit different properties. Some are soluble, while others float on water or may evaporate, affecting air quality or groundwater. Others are not soluble and may contaminate land or sink to the bottom of water courses to pollute sediment. Many of these compounds are associated with potential adverse health effects.

3. Heavy metals.

Heavy metals covers a large group of metals known or thought to be associated with environmental damage, including manganese, iron, copper, zinc, lead, nickel, cobalt, cadmium and chromium. The toxicity of these elements is well documented through a range of studies including analysis conducted by the WHO and national health agencies. Heavy metals are associated with increased risks of cancer and other chronic diseases. A number of these can also cause serious acute symptoms and are dangerous even at very low concentrations. For instance, chromium can cause serious pulmonary damage even at concentrations of just a few parts per million, while lead can cause organ, neurological and cognitive damage, especially in children, culminating in death at excessive levels of exposure.

4. Inorganic compounds and particulates.

These include gaseous compounds such as nitrogen dioxide, sulphur dioxide, carbon monoxide and ozone, as well as particulate matter. These pollutants are associated with respiratory diseases and, in high concentrations, can cause serious health effects. Gases like sulphur dioxide are also key contributors to acid rain.

5. Volatile Organic Compounds (VOCs).

This is a broad family of compounds generated primarily through industrial processes, such as the burning of hydrocarbons. Like heavy metals, many VOCs are highly toxic. For instance, two of the more common VOCs, benzene and benzopyrene, are high risk carcinogens strongly associated with the development of leukaemia. Moreover, even brief exposure to the former in high concentrations can lead to death within minutes, while lower doses can cause a range of symptoms, including tremors, elevated heart rate, vomiting and unconsciousness.

Human Health Impact Study

A second study was carried out to identify evidence of the health impacts of hydrocarbon pollution on individuals in Bayelsa. It was conducted among adults and children in four selected LGAs: Yenagoa, Kolokuma-Opokuma, Ogbia and Sagbama. For the purposes of the study, Yenagoa and Ogbia served as exposed LGAs, while Kolokuma-Opokuma and Sagbama served as the control.

Nine-person multidisciplinary study teams, including data collectors and laboratory scientists worked in each of the four LGAs. A cold chain was maintained throughout and analysis was undertaken in two processing laboratories, one in Nigeria and the other in Asia.

The study assessed and compared the blood levels of selected heavy metals and full blood count parameters in oil impacted and non-oil impacted communities in Bayelsa. It compared the morbidity pattern and incidence of cancer and other diseases in selected oil impacted and non-oil impacted communities in the state. It also used a cross- sectional comparative study design with a household survey and data abstraction from medical records leading to both primary and secondary data analyses.

The results are stark. The environmental impact study found high concentrations of dangerous toxins, far in excess of internationally recognised safe limits, across practically every site.

PAH levels exceeded safe values in virtually every sample taken, in some cases by considerable amounts. As indicated in the graphs that follow, every single ground water sample exceeded the recommended maximum safe level by at least 100 times, with one of the samples taken from Egbebiri exceeding the WHO limit by over 1 million times.

High levels of PAHs were also found in the surface water and sediment samples, as well as those of surface and deeper soils, and in most cases were significantly above safe limits. The study also found evidence that these concentrations had found their way into the food chain in a number of locations. In Egbebiri, as well as Ikarama and Kalaba, the analysis found that a number of species in the food chain, including catfish and crabs, all showed high concentrations of contamination.

A similar pattern of contamination was seen for TPHs. Virtually all samples breached safe levels. In the case of surface water, every reading taken was at least 300 times the maximum target value, with the samples taken in Kiminini exceeding the recommended maximum by over 700,000 times.222

An infographic showing that contamination was three hundred times the maximum target value safe levers. In Kiminini, contamination was seven hundred thousand times the maximum target value.

As indicated in the graphs below, every single ground water sample exceeded the recommended maximum safe level by at least 100 times, with one of the samples taken from Egbebiri exceeding the WHO limit by over 1 million times.

Polyaromatic hydrocarbons (PAH) in ground water and sediment and total petroleum hydrocarbons (TPH) in sediment and surface soil. The red line indicates the target value (WHO threshold).

A bar chart showing levels of polyaromatic hydrocarbons (PAH) in different areas, compared to the target values. The target value for PAH in ground water is 0.1 ug/l. Values found range from 570 ug/l to 47566 ug/l.
A bar chart showing levels of polyaromatic hydrocarbons (PAH) in sediment, compared to the target values. The target value for PAH in sediment is 1mg/kg. Values found range from 16.25mg/kg to 163mg/kg
A bar chart showing average total levels of petroleum hydrocarbons (TPH) in different areas, compared to the target values. The target value for PAH in ground water is 50mg/kg Values found range from 670mg/kg to 33392mg/kg
A bar chart showing average total levels of petroleum hydrocarbons (TPH) in surface soils, compared to the target values. The target value for PAH in surface soils is 50mg/kg. Values found range from 551mg/kg to 5098mg/kg

223

A similar pattern of contamination was seen for TPHs. Virtually all samples breached safe levels. In the case of surface water, every reading taken was at least 300 times the maximum target value, with the samples taken in Kiminini exceeding the recommended maximum by over 700,000 times.224

A bar chart showing PAH in surface water. In Kiminini levels were at 345000 ug/l.

With the exception of copper, the study found all other heavy metals at concentrations much higher than stipulated regulatory values at almost all locations.

Lead was found above regulatory limits at all locations, as was chromium; in many cases, the concentrations were dramatically higher than safe limits. For example, readings for chromium in ground water showed unsafe concentrations at every site, with every location on the Brass Canal exceeding the WHO target values by a factor of at least 40, and some breaching the values by over 1,000-fold.225 These results echo those reported in a 2013 International Union for Conservation of Nature (IUCN) study in Nembe, which found high levels of chromium in surface water, and high levels of both the metal and cadmium in sampled sediment and soil.226

Similarly, cadmium – which the WHO classifies as one of its priority poisonous metals – was found in the sample areas at levels which significantly exceeded regulatory limits, as was nickel, in the soil, groundwater and in the air.

Reflecting this, high concentrations of heavy metals were found in the food chain across testing sites, including chromium, cadmium, zinc, nickel and lead.

Two bar graphs showing the average lead and chromium in animal samples from selected sites. The amount of lead observed in crabs ranges from 0.2mg/kg to 0.92mg/kg. The amount of lead observed in catfish ranges from 0.14mg/kg to 0.65mg/kg. the amount of leaf observed in Bulinus spp ranges from 1.05mg/kg to 1.025mg/kg. The amount of Chromium observed in Crabs ranges from 1.14mg/kg to 1.2mg/kg, the amount of chromium observed in Catfish ranges from 0.19mg/kg to 1.08mg/kg. The amount of chromium observed in Bulinus spp ranges from 1.09mg/kg to 1.22mg/k.

227

Unsafe levels of some heavy metals were even found in the air. For instance, at Ikarama, nickel levels of 1.4 mg per cubic metre of air were recorded. Based on the readings taken across the test sites, Professor Jamieson estimates that Bayelsans inhale between 10 and 28 mg of nickel a day. According to the WHO, nickel inhalation induces respiratory tract irritation, chemical pneumonia and emphysema, as well as being carcinogenic. Given the health risks, the organisation states that ‘no safe level for nickel compounds [by inhalation] can be recommended’.228

Critically, but perhaps unsurprisingly given these results, levels of nickel and zinc exceeding safe limits were also found in the bloodstreams of test subjects in locations where blood samples were taken.229

Two bar graphs displaying the levels of lead and chromium in human tissue at selected sites. The normal level of Lead is 0.1mg/l and the first graph shows a range of entries from selected sites with a range of 0.45mg/l to 0.6mg/l. The second bar graph shows that the normal level of chromium is 0.014mg/l and the data from selected sites has a range from 0.25mg/l to 0.45mg/l/

230

While levels of inorganic compounds in the air were broadly within stipulated limits, VOC levels were problematic, exceeding safe limits with densities in the air sampled of between 350 and 750 parts per million (ppm).

These findings on air quality in Bayelsa corroborate and reinforce research undertaken in other parts of the Niger Delta. A 2019 study of gas flaring in communities around SPDC facilities in Gbarain Ubie in Southern Bayelsa showed that levels of all gaseous pollutants, with the exception of carbon monoxide, exceeded the limits set by Nigeria’s Ministry of the Environment.231 Even more alarmingly, levels of total suspended particulate matter exceeded government limits by between 10 and 15 times. These findings were corroborated by other studies showing particulate matter concentrations at four sites across the Niger Delta that significantly exceeded both Nigerian Government and WHO limits. Sulphur dioxide limits were also exceeded in some cases.232

These results were mirrored in part by the findings of the human health study.233 This study confirmed that people living in areas with higher levels of oil pollution had increased levels of zinc in their bloodstreams, although the levels of other metals did not appear elevated.

The study’s qualitative data also confirmed that those living in pollution-affected areas reported a higher prevalence of allergic reactions as well as acute and chronic illnesses. It also found that children living in affected areas were more likely to be underweight. These findings are consistent with those of a previous independent study that analysed four years of medical records taken from communities exposed to gas flaring.234

Taking all the scientific findings together, the evidence from the Commission’s testing is clear. Toxins from hydrocarbon pollution are present at often dangerous levels in the soil, water and air across Bayelsa. They have been absorbed into the human food chain. And they have ultimately found their way into the bloodstreams and tissue of people living in affected communities.

A photograph of a man standing in a boat next to contaminated water holds up a dead and bloated fish carcass.
Dead fish in contaminated water near an Agip flow station. Fishing is an important income source and a local staple food.

Counting the costs – the consequences of pollution

Decades of oil pollution have bequeathed Bayelsa a toxic legacy, with testing showing an environment saturated with harmful pollutants. This legacy has imposed huge costs on the state and its people.

The environmental cost

The pollution crisis has had a devastating effect on almost every facet of Bayelsa’s environment. Internationally, decades of research has charted the highly adverse impact oil pollution has on wildlife and the natural environment. This section seeks to provide a snapshot of some of the evidence the Commission has seen and give a sense of the scale of the environmental disaster that has unfolded.

Chapter One introduced the Niger Delta’s unique landscape of swamp, mangrove forest, farmland and waterways. The Niger Delta, which boasts the largest mangrove forest in Africa and the third largest globally, is Africa’s largest wetland. 80 percent of the Niger Delta’s 12,000 km2 of mangrove vegetation is distributed across just three states – Bayelsa, Delta and Rivers.235 As much as 36 percent of Bayelsa’s total landmass – over 3,500 km2 – is covered by mangrove forests. It is an area of immense environmental value, acting as a key biodiversity hotspot and providing a critical habitat for the animal and plant life upon which so many of the state’s residents depend.

But the Niger Delta’s ecosystem is also intensely fragile. Since oil production began, up to 40% of the Niger Delta’s mangrove forests have been lost.236 This translates into the loss of 2,500 km2 of forest area in Bayelsa alone.237 A 2016 study found that the Niger Delta accounts for 27% of all mangroves around the world that are potentially threatened by oil spills.238

While other factors such as over-harvesting of timber have exacerbated the damage to the region’s mangroves, oil pollution and activities associated with the oil industry, such as waterway dredging and the removal of barrier islands, are among the primary causes of forest destruction. Development of oilfield infrastructure in the mangrove areas of the Niger Delta is often preceded by dredging and/or vegetation clearance to create navigable accesses. During dredging, the soil, sediment and vegetation along the right of way of the proposed site are removed and typically disposed of over bank, and in most cases upon fringing mangroves, and then abandoned. Abandoned dredged material has altered topography and hydrology and led to acidification and water contamination, all of which has resulted in vegetation damage and loss of marine life. After several years of natural weathering, former mangrove areas have become altered into either bare heaps, grassland or freshwater forest. The altered topography has, among other factors, also prevented the natural re-establishment of lost mangrove forests.239

The extent of local deforestation has driven broader negative shifts in many of the state’s wetland ecosystems, with the loss of canopy cover and sediments that the mangroves anchored, leading to a loss of habitat for a broad range of animal and plant life. 240 Tropical forests are complex ecosystems and when destroyed or polluted recover only slowly at best.241 Mangroves are not only crucial in providing protection against marine erosion and salt intrusion but are indispensable to the reproduction of many fish and crustacea which are central to the livelihood of Delta communities.242

his dynamic has been reinforced by some of the other effects of oil pollution, both direct – through the poisoning of populations and the introduction of dangerous toxins into the food chain – and indirect, for instance through the inhibiting of photosynthesis and the reduction of oxygen levels in waterways.243

During its evidence-gathering sessions in Bayelsa, the Commission heard individual accounts of environmental destruction as a result of oil production.

“  ”

As a young girl, we used boats to go to the forest to pick periwinkles and to kill crabs, prawns, crayfish and oysters. But when I got to secondary school, all we saw was oil in the forest. As the water flows, it takes the crude oil everywhere. No more periwinkles to pick again. No more crabs in the river.

Community leader
Twon Brass

“  ”

We can no longer teach [our children] how to pick periwinkle. Even crabs cannot be found again. All our children see is crude oil flowing into the creeks and farms and rivers. The bitter leaves and pepper that we plant are not growing again.

Female
Twon Brass244

“  ”

There are crude oil points, and when the pipeline is bad, the whole place is uprooted and made barren. When we were young, we saw white and colourful birds...but now you cannot count one.

Fisherman and community leader
Akassa245

“  ”

The land no longer supports farming as crops do not grow anymore. Some species of fish have disappeared from the rivers of the community. When it rains, we used to catch water, but this is no longer the case, as when you collect rainwater, it is filled with chemical sand and black objects.

Traditional ruler, Okoroma Clan
Nembe LGA246

Similar stories were heard during the Commission’s visit to the Aghoro community concerning spills over the last twenty years that led to the permanent destruction of mangrove creeks.

Once known for its thriving fisheries, Brass’s landscape has been decimated by oil pollution. A fisherman spoke of the change he has seen over 40 years.

Oil production has led to the destruction of the natural environment through dredging, vegetation clearance and pollution.

A photograph of a polluted riverbank, there is a black line of dead vegetation at the water level line.

Oil spill in Ekeremor LGA, Bayelsa, 2018

In Ekeremor LGA, a community leader reported concerns to SPDC in May 2018. She raised the alarm over the oil spill from the Trans Ramos pipeline and also about the alleged intimidation of community leaders of Aghoro 1 who were involved in the investigation of an oil spill that occurred in the area. The spill caused destruction to aquatic life and hardship for the communities who had no fresh water to drink for several weeks.

A reconnaissance visit by members of the BSOEC Secretariat to Ekeremor in 2018, prior to the establishment of the BSOEC, saw a site devastated by the oil spill, with the local communities concerned that they had not been supplied with fresh water, and that their children were reporting strange illnesses. Only when the incumbent Deputy Governor of Bayelsa State visited the spill site with national media and some much-needed relief materials for members of the community such as drinking water and food, concerted efforts to address the spill began.

The community leader said “they have contaminated our communities and we have no drinking water. All the fish and mangroves have died and they want to force us to sign a JIV report. We will not accept this.”

A visit by the BSOEC to the community in November 2019 reported that the spill was still continuing, 18 months later.

The clean-up and remediation were completed on 21 February 2020.247

In Yenagoa LGA, the Commission heard that in the past, the river was dredged without community consent for one year, which led to the community suffering from frequent flooding and constant river bank erosion with land and, eventually, houses lost over a number of years. Similarly, rain water used by local people was said to be contaminated from nearby gas flares that burn daily. In a site visit to Southern Ijaw, the Commission witnessed the environmental degradation first-hand. During a visit to Oyeregbene, the Commission was told that oil had repeatedly spilled from an 18 inch Eni (Agip) pipeline, leading to devastation of adjacent mangrove swamps that were stripped of mangroves, foliage and vegetation.

A poor clean-up attempt by Eni (Agip)

The Commission personally witnessed the damage caused by oil spills during several visits to the Egbebiri and Okordia communities in Bayelsa. A team led by the Commission’s Chair, former Archbishop of York, Lord John Sentamu, in 2018, examined the environmental destruction caused by equipment failure at a local well operated by Agip (Eni), that led to an estimated 200 barrels of crude oil being spilled. The Commission was appalled by what they found. The spilled oil had affected an area covering 5,420 metres and destroyed local vegetation and wildlife.

A further trip in 2019 to the same site, resulted in the Commission finding 20-30 members of an Eni clean-up crew. The leaders of the clean-up crew were speaking amongst themselves and asking who the visitors were. Bishop Lord Sentamu who spoke Arabic translated to the Commission that they said the workers were having to clean-up as a result of an “interfering priest that had visited the site”. Bishop Lord Sentamu informed the crew that he was that “interfering priest”.

Unfortunately the Commission saw that the clean-up crew’s efforts – which the Commission believed were expedited due to their visits – were not going to leave the affected communities any better off. The crew was scooping up the oil from the pond and pouring it into a hole that they had dug on land and burning the oil in the hole. This was an illegal activity that would have resulted in the oil seeping into the ground and groundwater. A neighbouring community complained that their yams had shrunken and/or were growing disfigured.

The resulting impact of environmental pollution is often a dramatic fall in critical animal populations. A 2003 study on the impact of pollution on turtle numbers across the Niger Delta found that the turtle population was almost six times lower in polluted areas.248

Similarly, research on the impact of two major spills in neighbouring Rivers State found a 91 percent decline in the number of species after pollution incidents.249 Key populations that anchored the ecosystem and provided an important source of food for both marine life and humans were completely wiped out.250

In 2015 during a visit to Ekeremor, after the Commission navigated through the creeks in Bayelsa for five hours, Bishop Lord Sentamu remarked at the end of the day that he had not seen a single bird on the Commission’s journey that day. What should be a lush environment for flora and fauna, was entirely barren.

It is not just waterways that have been contaminated, farmland has been destroyed too.251 As will become evident in the next section, oil sector activity has introduced toxins into the human food chain and significantly reduced the yield of affected farmland, thereby contributing to a loss of earnings and food insecurity.252

Pollution’s effects on the Niger Delta and Bayelsa are not just extensive, but also long lasting. A 2011 United Nations Environment Programme (UNEP) report on the impact of oil pollution in Ogoni in neighbouring Rivers State, found that 18 years after oil production in that region had ceased, the impacts on the environment would take as much as 30 years to be ameliorated.253

The absence of a similar full assessment of the extent of environmental pollution in Bayelsa was lamented by many of those the Commission met with, and is one of the main reasons why the Bayelsa State Government took the decision to set up the Commission. Whilst the Commission has been able to make significant strides in shedding light on Bayelsa’s environmental problems, the need for a full environmental assessment of Bayelsa remains.

A photograph of a shallow pool of water clearly contaminated with a film of black oil and piles of dead reeds and vegetation.

The economic and social cost

The degradation of Bayelsa’s environment has implications that go significantly beyond the destruction of the local natural biosphere. In a state where 75 percent of the population rely on subsistence agriculture or fishing to make a living, pollution and its impacts have huge ramifications for local peoples’ livelihoods.

Research across the globe demonstrates that oil pollution dramatically reduces the incomes of affected communities, and the Niger Delta is no exception. The evidence is stark. A study of 13 fishing communities affected by oil pollution in the Niger Delta found that 88 percent of respondents saw their businesses fall into loss following oil spills. Catches and income dried up completely in the immediate aftermath of spills and only recovered slowly after remaining depressed for years after the events. The significant loss of livelihood following spill incidents led 43 percent of respondents to change their means of subsistence and another 25 percent to consider abandoning their current business.254 As well as reducing incomes and employment in the area, spills had also driven price rises that local people could ill afford, as goods that were previously sourced locally had to be brought in from outside.

Much of the available data on economic effects comes from neighbouring Rivers State due to high-profile court cases related to instances of pollution. In Bodo, a host community known for suing Shell for oil spills, a comparative study found that incomes from shellfish collection in the polluted areas of the Creek were only roughly 40 percent of those generated in comparable non-polluted communities.255 The spills in these areas wiped out the periwinkle population. A post-spill study of the area did not find a single living specimen, resulting in local women who had previously generated incomes of 500 Naira (US $1.22) a day from harvesting them being forced to find other employment in a neighbouring state.256

In Bayelsa, studies conducted over the last few decades have highlighted the devastating impacts of oil pollution and gas flaring on livelihoods. A survey of 150 respondents on the impact of gas flaring in Ogbia LGA published in 2009 found that over 40 percent of the respondents believed that gas flaring undermined their socio-economic wellbeing. In addition, farm households claimed that flaring by oil companies in Ogbia reduced their agricultural output and income from farming activities.257 Another study on the impact of oil pollution in the Epebu community, also in Ogbia LGA, concluded that oil spillage had greatly affected the livelihoods of the community’s people by destroying forests and trees, causing untold damage to economic activities and agricultural production along with destruction of fish stocks in ponds and other waters.258 Specifically, prolonged gas flaring, oil spillage, and other forms of pollution have decimated local wild palm trees. In addition, the extension services of the Nigerian Institute of Palm Oil Research (NIFOR) in Bayelsa have been affected by the degradation of the environment by the oil companies. As a result, the tapping of palm trees has virtually ceased and poor harvests have also been experienced by farmers across the state to the extent that they have had wider negative impacts on food production.259

The effects of spills are not just confined to fishing. A 2012 study in Rivers State found that polluted crop farms had an average output 22 percent lower than those that had not been exposed to pollution.260 This tallies with evidence from the Bodo spills, where a 2011 report found that average yields for staples such as yams and cassava fell dramatically after a pollution incident and remained depressed for a number of years afterwards.261

These findings are supported by research into the production rates of 262 farms across neighbouring Delta State, lying to the west of Bayelsa, which confirmed that as spill intensities rise, yields fall. Typically, a 10 percent rise in pollution depressed yields by a corresponding 5 percent.262

These deleterious effects are not limited to oil spills only, as a wide range of polluting activities have generated negative impacts across the length and breadth of the Niger Delta. A study from Imo State found that crops grown within 200m of a flare station suffered a 100 percent loss in yield, while those grown 600m away from the station saw their yield plunge by 45 percent.263 Even farmland a kilometre away from the flare experienced a 10 percent fall in its output.264

Other research has also found significantly elevated incidences of toxins in crops farmed on tainted land with, for example, increased levels of lead and cadmium by as much as 90 percent and 94 percent respectively in local pumpkins. The same study found that crops farmed on contaminated land have a far lower nutritional content, with the protein content of cassava, for example, being reduced by 40 percent in samples taken.265

In 1995, author and campaigner Ken Sarowiwa was charged with incitement to murder and was executed by Nigeria’s Military Government. Shell, in 2009, agreed to pay US $15.5m (£9.6m) out of Court in a settlement of a legal action – reached on the eve of the trial in a Federal Court in New York – which accused Shell of collaborating in the execution of Ken Sarowiwa and nine Tribal Leaders (the Ongoni Nine). 900

Community testimonies

These studies echo the testimonies the Commission has heard from across Bayelsa about the ruinous effects of oil pollution on the ability of families and communities to support themselves. A small sample of these stories is outlined in the box below.

BSOEC HEARING, OGBIA

“  ”

The community has suffered from air pollution and infants have been the worst impacted; there are several cases of rashes on children due to gas flaring and spills. Also, the waterways used to be livelihood structures that supported livelihoods like fishing.

Community leader
Otuokpoti

BSOEC HEARING, BRASS

“  ”

We have a lot of problems from this oil and gas pollution. If you go to the waterside, you can see how we are suffering; we cannot catch fish again, the fish is polluted, you can’t make money from the river because of the pollution.

Traditional ruler
Twon Brass

BSOEC HEARING

“  ”

The air is highly polluted and it has affected the respiratory systems of community folks. The river is polluted and communities can no longer drink from the river. This has affected aquatic life and fishing is no longer productive.

Community leader
Imiring

BSOEC HEARING, BRASS

“  ”

All our children see crude oil flowing into the creeks, farms, and rivers. The bitter leaves and pepper that we plant are not growing again. Help the women of this highland.

Community leader
Twon Brass

Bayelsa’s population has historically depended on agriculture and fisheries. More than 60 years of oil and gas industry activity and associated pollution, combined with the diversion of water sources to make hydrocarbons extraction possible, has severely disrupted agrarian productive systems.266

The scale of oil contamination has had a significant impact on the economics of Bayelsa and the livelihoods of some of the state’s poorest people. At site visits and evidence gathering sessions, the Commission heard testimony and received written submissions describing how individuals and communities had lost their farming and fishing livelihoods and had been reduced to destitution as the result of oil related pollution.

Across Bayelsa, people interviewed by the Commission complained of the lack of employment opportunities with oil companies, despite having the requisite skills, and refuted IOC claims that opportunities are available to local people. The Commission heard how in Ogbia LGA, "host communities cannot boast of [being] even drivers employed by Shell”, and in Brass LGA, local people reported how “they [the oil companies] have employed people from outside this island, but not the host community”.

Despite oil companies offering to up-skill and train those in host communities, the Commission heard frustrations and anger expressed about perceived economic injustices resulting from projects not completed and promises left unfulfilled.

A close up photograph of very polluted water, there is a thick sludge of black oil on the surface and lots of dead reeds

“  ”

Farmlands are affected...the natural canals are now blocked...my people are suffering as a result of what Shell is doing.

Community leader, Ofoni
Sagbama LGA267

“  ”

We are supposed to have skills centres in our communities... There is an abundant presence of oil and gas in the Niger Delta, but is the wealth felt by the communities?

Resident
Kolokuma LGA

“  ”

I have ponds and fish traps that have all been damaged by the crude oil. I depended on them as part of my means of livelihood. The fishponds that are now covered with crude oil are also what I normally looked forward to harvesting, with hope. Now, my hope is dashed. Who will help me?

Fisherman
Ogbia LGA

“  ”

Fishing, which is our major occupation, has been adversely affected as we cannot go to the river again to fish as we ought to.

Resident, Aghoro
Ekeremor LGA

Moreover, the loss of livelihoods is all too often accompanied by an increase in the price of basic staples, as more food stuffs have to be brought in from outside the community. This double whammy of falling incomes and rising prices as a result of spills has driven sharp rises in local food insecurity and malnutrition. A large-scale study conducted across Bayelsa found that only 3 percent of those living in communities that had suffered an oil spill were food secure as against 67 percent in non-spill affected communities. The research also found that 47 percent of children in oil polluted communities in one part of the state are underweight, more than double the rate for south-west Nigeria as a whole.268

This confirms what countless witnesses have told the Commission: oil pollution has deepened poverty in communities that are already struggling to get by and the primary victims have been children.

Pollution has contributed to the rise of artisanal refining, as more people, deprived of their livelihoods, are forced to partake in the oil theft industry themselves, potentially participating in pipeline sabotage and perpetuating the cycle of pollution and loss of traditional livelihoods.

Unfortunately, the economic impact does not stop there. The tensions caused by loss of livelihoods have caused the social fabric, already strained in many of these communities, to further break down, often violently. The Commission has heard repeated evidence that pollution has forced many people to travel far outside their local area to find employment or new fishing grounds, often bringing them into conflict with other established communities. In the case of those affected by the Bonga oil spill in 2011, this oil-enforced migration had tragic consequences, as fishermen in search of unpolluted waters crossed into Cameroonian waters, sparking a conflict that cost a number of lives.269

These same dynamics have fuelled depopulation, with villagers from polluted communities often forced to migrate to urban centres in search of alternative livelihoods.270 Against this backdrop, research shows that traditional practices that are important for the maintenance of community cohesion, like communal fishing, have gone into steep decline in polluted communities.

Transaction costs remain inordinately high due to poor infrastructure and the cost of transporting goods by speed boat, while oil companies provide the only viable local market for any kind of productive activity and trading in the riverine/swampland communities. At the same time, competition for scarce and selectively distributed resources by IOCs that trickle in from compensation and remediation payments has increased, fuelling additional conflict within local communities themselves. As will be outlined in subsequent chapters, deep flaws in the operation of GMOUs and the way IOCs engage with affected communities have exacerbated both inter- and intra-communal polarisation and violence. 271

The Commission heard testimonies and received evidence about deep divisions in communities allegedly created by IOC’s through selectively favouring particular groups against others as a means of undermining claims for clean-up or compensation.272

Testimony at Oporoma Community Hall

“  ”

JIVs do not integrate community inputs. Use of legal redress is frustrating and expensive for communities and oil companies rely on military repression of communities. They also use divide and rule to enable them to continue clamping. They are also supposed to come back for clean-up and remediation. They send some money to make us fight ourselves and end up doing nothing on the site.

Oporoma Council of Chiefs
Southern Ijaw LGA

Extract from Witness Statement for Bodo Community vs SPDC

“  ”

...In my view, much of the misinformation circulating in the community which led to unrest could have been prevented by a transparent and rigorous approach to the appointment of contractors and community sensitisation. But that was not how SPDC... operated.

David Little
Independent Researcher

“  ”

Shell admitted that it was equipment failure. I am surprised to know that up till now Shell has not relieved the suffering of the people. Shell is not following best practices. Close to Agbura and Otuokpotidi there was a spill that occurred during the flood. When it occurred like that, it took the oil to the Atlantic Ocean. Shell did divide and rule. We petitioned Shell at the FGN. We wrote to the AGF and the Minister of Environment. Since 2016 they have done nothing.”

Male Resident, Ayama
Ogbia LGA 273

The decline of traditional livelihoods, the expansion of a transient workforce, and instability within and between communities through the unravelling of social ties impede the development of local economic systems while driving growth in the exploitation of people who are already vulnerable. Women and young girls have been made particularly vulnerable to sexual abuse in many communities where oil workers have had access.274

Particularly disturbing, the Commission gathered documentation and testimony concerning the ongoing allegation of sexual abuse of minors by oil company staff at multinational oil company facilities, in particular with reference to the Gbarain Ubie gas plant. These social issues require ongoing attention and investigation.275

Julie Okah-Donli, the former Director General of the National Agency for the Prohibition of Trafficking in Persons (NAPTIP), confirmed high levels of sexual exploitation of girls in Bayelsa State at the hands of oil and gas workers.276 Although there were numerous reports of exploitation to NAPTIP and many cases were taken to court, most never saw the light of day as poor and vulnerable families would accept settlement offers from defendants to drop the cases.

A photograph of two people posing in front of a field that has been contaminated by oil pollutants.
Members of the communities that the BSOEC visited were willing to share their stories and the impact of living with oil pollution.

Testimonies given to the Commission in Bayelsa, corroborate research conducted in neighbouring Delta states.

“  ”

Itinerant oil field workers find the teenage girls in their immediate host communities a ready pool with which to gratify their sexual urge. In each exploration site, these migrant oil workers leave behind an amazing corpus of venereal diseases and morally polluted girls and school drop-outs. Likewise, the displacement of certain villages in the Niger Delta has seriously affected their social and cultural lives.277

His Royal Majesty, King Bubaraye Dakolo, Agada IV, the Ibenanaowei of Ekpetiama Kingdom testified before the Commission, on 29 March 2019. In this testimony he recounted how rape, underage sex with girls as young as 12, and unwanted pregnancies, were commonplace. He repeated calls made in 2017 (to no avail) to UNICEF and the NAPTIP to investigate and even offered to pay for their visits to Bayelsa.

“  ”

And right in front of that facility, there is some kind of ghetto. I don’t know how it came about, but those kinds of ghettos follow every oil activity in the Niger Delta. No sooner than they had come there, they invited people from everywhere to come there, and what you see there are drugs being sold and traded, and girls – under-age ones – being sold and traded along, and women of all types being sold and traded, and youths of all types being lured into criminality. You can imagine if you’re exposed to products that are not familiar to you. We do not have any factory that produces amphetamines of any type, no factory for tramadol, no factory for cocaine, and so on and so forth. Perhaps the only thing that will grow and has been growing around here in the last couple of years since oil came, has been the one they call igbo. Igbo is marijuana. That one grows so well, so once the oil workers bring them and they smoke them and they leave the seeds around, they grow on their own. And of course, if you work as a servant to one of these oil workers, no sooner than you can imagine, you are now also lured into drugs and then you become a drug addict. So, many youths become drug addicts, and, of course, if we are talking about 60 years, some of those youths are now 60-year-old men, 50-year-old men, 30-year-old men and 25-year-old men.278

This content was used in a press of interview in 2017 and now the subject of a book-length publication in 2021.279

“  ”

Yes, most oil workers in my kingdom and other areas around here have this sexual perversion in which children are the preferred sexual objects. But, as disgusting as this may sound, they do not seem to have any remorse about what they are doing. When they get into a community, they lure very young girls between the ages of 12 and 14 years to bed. They make them some kind of sex slaves, luring them with money. Too many men and too few girls. They do this to girls in primary schools and Junior Secondary (JS1). They thereby destroy the social environment they find themselves in. This is so bad and grave a crime that one can’t properly quantify it in terms of Naira and Kobo.

Sexual Abuse

Extracts from King Dakolo’s book The Riddle of the Oil Thief:

“  ”

Within weeks of being around, they completely disorganised the social equilibrium the community had enjoyed for so long. Their workers could not restrain their libido and started committing all kinds of sexual atrocities, using their superior financial advantage. Before anyone could spell bingo. Even the headmaster who was thought to be rich could not match the least of them financially. After barely four months of their stay, calamity was wreaked upon the community. It was discovered that a lot of underage girls had been impregnated by oil workers who sneaked into the community at night ....

They had their speedboats handy to facilitate those clandestine trips designed to gratify their viagra-induced libido. With their speedboats, nearby communities suffered equal or worse ravaging. With national regulators who are accomplices in the underdevelopment of the oil-bearing and facilities hosting communities, the oil companies do not bother to be ethical or obey rules in place for the protection of vulnerable natives. But what was the IOC’s intention in sending four thousand devourers, armed with biologically potent warheads, without their wives or female colleagues, and without arrangements for weekly time-off, to a vulnerable and oil-bearing facility hosting little community? Theirs was just the oil for the money and nothing for the people. As a matter of fact, the IOCs, the regulators, and the security agencies all see the people of the oil-bearing or facilities hosting communities as obstacles to their anti- people business of oil and gas in the Niger Delta of Nigeria. For them, people have too many prying eyes, watching their every move, and that is not good. The people could as well get destroyed by the ruthless, so long as there is no evidence left as fodder to ignite public uproar. Like heinous war-crimes, the people can be destroyed provided their story remains untold. The oil-bearing and facilities hosting people could be destroyed as long as the secret does not leak out to the world and as long as it remains a ‘perfect’ crime!

A photograph of a green field, in the distance there is a large compound of oil extraction machinery and pipelines

The cost to human health

The human suffering inflicted by the pollution catastrophe that has befallen Bayelsa is measured not just in terms of incomes reduced or communities fractured. It is also measured in lives cut short.

“  ”

The community has continued to suffer the health impacts.

Community leader
Obuna280

The intensity and sustained nature of the pollution communities are exposed to has fuelled a silent health crisis. The scale of the crisis demands ongoing research and careful monitoring, something which industry has sought to avoid all over the world to prevent class action proceedings. But independent research suggests that the toll across the Niger Delta could run to hundreds of thousands of deaths, with countless more lives ruined by chronic disease. The price paid in human suffering for the failure to tackle oil pollution and its health effects has been simply extraordinary.281

BSOEC Hearing, Yenagoa

“  ”

I work at Otuasega hospital. I have worked there for about 10 years. I have seen a lot of people who have issues which reflect the third and second presentations. Respiratory illnesses and skin lesions are slightly different from other places. Asthmatic attacks: sudden asthma as well as respiratory issues. I can also say that the level of spontaneous abortions has increased as well as infertility. Semen analysis shows the sperm count has drastically reduced over time.

Health practitioner
Ogbia

The connection between key types of hydrocarbon contamination and both chronic and acute conditions is well established as previously illustrated. Evidence shows dangerous levels of toxins in the land, groundwater and crops across Bayelsa and their accumulation in the human food chain and ultimately in the local population itself. Across each of Bayelsa’s eight LGAs, there is repeated testimony of medical conditions resulting from exposure to oil spills, ranging from skin rashes and respiratory illnesses to pneumonia.

One member from the coastal community of Ekeremor LGA described sickness that engulfed her family as a result of an oil spill that occurred in May 2018:

“  ”

The spill spoiled the water. We could not bathe or drink the water. The spill killed the fish in the river. This caused a lot of sicknesses in the community and it killed a lot of people. Many children died because of the spill. We cannot do otherwise than starve. We waited for relief materials and only a few people received them.282

Community member
Ekeremor

This testimony confirmed earlier accounts collected of surface, ground water and soil contamination with hydrocarbons, heavy metals and other toxic chemicals:283

“  ”

There were reports of gastroenteritis; we experienced more children being rushed to the Health Centre recently, even elders are affected. If you go into the communities you will see measles cases too... and this could come from pollution in the air.284

Similarly, in the Apoi community in Southern Ijaw, a large spill of crude oil in 2017 from an Agip facility had devastating impacts on the local community:

One elderly fisherwoman was said to have fallen into the oil spill-affected swamp and experienced a “pepper sensation” and “peeling skin" for weeks afterwards. Another resident stated that

“  ”

We cannot even drink the water in the swamp or engage in the special rainy season fishing in the swamps anymore.285

The consequences for the health of the population of the sustained exposure to a cocktail of pollutants have been sobering.

Today, life expectancy in Bayelsa is a mere 50 years at birth, 286 three years less than Nigeria as a whole and among the lowest of any state in the Niger Delta. At a time when mortality and morbidity rates have fallen in the rest of the country, Bayelsa has seen theirs remain stubbornly high, with an infant mortality rate of 31 per 1,000 live births. 287

A table displaying the infant mortality rate per 1,000 live births. In Bayelsa 31 infants die per 1,000 live births, in Europe 3, In the UK 4, in the US 6

288

While oil pollution is not the only factor, it is among the key driving forces, contributing directly to elevated levels of chronic disease as well as to raised levels of malnutrition that push up mortality rates, in particular among children, in communities without the resources to cope.

Perhaps most shockingly, recent research suggests that exposure to oil spills before conception killed around 16,000 infants within the first month of their life in 2012 alone. There is no reason to believe that 2012 was special. If these results were reflective of other years, this suggests that pollution has led directly to more than 100,000 additional neonatal deaths in the last 15 years alone. And Bayelsa, at the epicentre of the pollution crisis, will have borne much of the suffering.289

Compounding the tragedy, Bayelsa’s healthcare system lacks anything like the capacity to tackle the silent healthcare crisis endemic pollution has created. Only 5 percent of households have health insurance. As a result, many families are thrust deeper into poverty by oil-related health problems. According to a 2018 study in the state capital, Yenagoa, additional healthcare expenditure resulted in almost 10 percent of households being pushed below the poverty line while another 9 percent who were previously poor were pushed even deeper into extreme poverty.290 Moreover, even when families can find the money for healthcare, it is often of low quality. Only 6 percent of clinics in the state have a doctor and only 18 percent have any form of trained medical staff. While there are 168 clinics across the state on paper, many are barely functioning, closed or even derelict.291

A recent study of Total Suspended Particulate Matter (TSPM) across Yenagoa LGA recorded TSPM concentrations that significantly exceeded WHO and Nigerian federal standards at four sampling sites, with the highest levels of toxicity found at Gbarain Ubie.292 A 2019 study of gas flaring in the communities surrounding the Gbarain Ubie gas processing plant found that, with the exception of carbon monoxide, the concentration of gaseous pollutants in air samples in the region exceeded the standards of Nigeria’s Federal Ministry of the Environment.293 At their highest reading, TSPM concentrations – a cause of respiratory and cardiovascular disorders – surpassed the Nigerian federal standard by almost 10 times during the wet season and 15 times during the dry season.294 In addition, sulphur dioxide concentrations at most study locations exceeded the federal standard during dry periods.295 In all the locations in the study area, VOC concentrations in both wet and dry seasons have been in breach of the Federal Ministry of Environment’s standards.296

A multifaceted crisis

The unprecedented tide of pollution that has engulfed Bayelsa has spawned separate, mutually reinforcing crises affecting the local environment, economy, populations and public health. They have combined to inflict tremendous hardship and suffering on the people of the state.

Such a tide of pollution would never be tolerated in the home countries of the large international oil companies. Yet it has been allowed to carry on unchecked in the Niger Delta. So why has Bayelsa suffered such extraordinary levels of pollution? Chapter Three will examine the causes.

PAGE SECTIONS
Chapter icon
  1. OECD. n.d. Glossary. [Accessed 14 November 2022]. Available at https://stats.oecd.org/...

  2. Schlumberger. n.d. Energy Glossary [Online]. [Accessed 14 November 2022]. Available at https://glossary.slb.com/...

  3. NetRegs. n.d. Trade effluent – Managing liquid wastes. [Accessed 14 November 2022]. Available at https://www.netregs.org.uk/...

  4. Onuh, P. A., Omenma, T. J., Onyishi, C. J., Udeogu, C. U., Nkalu, N. C., and Iwuoha, V. O. 2021. Artisanal refining of crude oil in the Niger Delta: A challenge to clean-up and remediation in Ogoniland. Local Economy, 36(6), pp. 468–486. [Accessed 14 November 2022]. Available at https://doi.org/10.1177/...

  5. According to the NOSDRA Oil Spill Monitor, which covers less than 15 years of oil and gas activities in the Niger Delta, a total of 3,300 spills have affected Bayelsa state since 2006, amounting to approximately 106,107.89 barrels of hydrocarbons. If gas is also treated as a contaminant, a further 39 spills are included in the total. The 3,300 spills at over 100,000 barrels makes up more than 25% of all spills in Nigeria recorded by NOSDRA since 2006. [Accessed 25 February 2021]. Available at https://nosdra.oilspillmonitor.ng/

  6. Vidal, J. 2010. Nigeria's agony dwarfs Gulf oil spill. The Guardian [Online]. 30 May. [Accessed 30 September 2020]. Available at https://www.theguardian.com...

  7. Vidal, J. 2010. Nigeria's agony dwarfs Gulf oil spill. The Guardian [Online]. 30 May. [Accessed 30 September 2020]. Available at https://www.theguardian.com...

  8. Cassidy, E. 2019. "There were 137 oil spills in the US in 2018. See where they happened." Resource Watch [Online]. 7 February. [Accessed September 30, 2020]. Available at https://blog.resourcewatch.org.... But there were 2000 ‘petroleum spills impacting navigable waterways in 2018, see Bureau of Transport Statistics. n.d. "Petroleum Oil Spills Impacting Navigable U.S. Waterways." United States Department of Transportation [Online]. [Accessed 10 July 2021]. Available at https://www.bts.gov/conten....

  9. Cech, M., Davis, P., Gambardella, F. and Haskamp, A. 2019. Performance of European cross-country oil pipelines: Statistical summary of reported spillages in 2017 and since 1971. Concawe Report. Brussels. June 2019. [Accessed 29 August 2022]. Available at https://www.concawe.eu/w... Own calculations based on CONCAWE reports on reported spillages between 2006 and 2020.

  10. Theodora.com. 2017. Nigeria pipelines map - Crude oil (petroleum) pipelines - natural gas pipelines - products pipelines [Online]. Countries of the World. [Accessed October 4, 2020]. Available at https://theodora.com/pipeli... In neighbouring Rivers State, Bodo, an average of 33.3 spills per year per 1,000 kilometres has been cited as attributable to SPDC. This is 133 times higher than the European average over the period of 2006-2010 for spills of any cause; Berebon & Ors vs Shell Petroleum Development Company of Nigeria Ltd. High Court of Justice Claim No. HQ12X04933 HT-13-345, Queen’s Bench Division. Bomu-Bonny Oil Pipeline Litigation; Cech, M., Davis, P., Gambardella, F. and Haskamp, A. 2019. Performance of European cross-country oil pipelines: Statistical summary of reported spillages in 2017 and since 1971. Concawe Report. Brussels. June 2019. [Accessed 29 August 2022]. Available at https://www.concawe.eu/w...

  11. Cech, M., Davis, P., Gambardella, F. and Haskamp, A. 2019. Performance of European cross-country oil pipelines: Statistical summary of reported spillages in 2017 and since 1971. Concawe Report. Brussels. June 2019. [Accessed 29 August 2022]. Available at https://www.concawe.eu/w...

  12. Watts, M. and Zalik, A. 2020. Consistently unreliable: Oil spill data and transparency discourse. The Extractive Industries and Society, 7, pp. 790-795. While the NNPC figures referenced above are much higher than NOSDRA's, the DPR figures cited in Ejiba, I.V., Onya, S.C. and Adams, O.K. 2016. Impact of Oil Pollution on Livelihood: Evidence from the Niger Delta Region of Nigeria. Journal of Scientific Research and Reports, 12, pp. 1-12, are considerably lower than NOSDRAs. NOSDRA records a total-barrels spilled figure greater than double the DPR figures cited therein. See also Yeeles, A. and Akporiaye, A. 2016. Risk and resilience in the Nigerian oil sector: The economic effects of pipeline sabotage and theft. Energy Policy, 88, pp. 187-196.

  13. Based on data in the NNPC’s report, there were over 35,000 incidents across Nigeria as a whole between 2005-2018. To obtain an annual rate the data is divided by 13 years (the period over which the NNPC has gathered data for Nigeria as a whole), equals an annual rate of 2,739. Annual rate 2739 x 14 years (the data period for NOSDRA) = 52041 x 0.26 (Bayelsa’s proportion of Nigerian oil and oil spills) = 13,531 /19 =714 per year. Bayelsa spill incidents every year = 714 spills (hours per year = 365 x 24 = 8,760. 8,760 hours / 714 spills. The calculations suggest Bayelsa has suffered a leak every 12 hours over that period. See Nigeria National Petroleum Corporation. 2019. 2019 Annual Statistical Bulletin. NNPC ASB 2019. 1st Edition. [Accessed 3 October 2021]. Available at https://www.resourcedata.org...

  14. NOSDRA. n.d. Nigerian Oil Spill Monitor. [Accessed 27 December 2022]. Available at https://nosdra.oilspi...

  15. Watts, M. and Zalik, A. 2020. Consistently unreliable: Oil spill data and transparency discourse. The Extractive Industries and Society, 7, pp. 790-795. Over the period 1999-2004 (following the return to civilian rule) pipeline product losses amounted to an astonishing 1,854,000 metric tons (13.2 million barrels) from 4,426 events, of which 85 percent were in the Warri and Port Harcourt zones; 5.2 percent were attributed to ‘rupture’ and 94.8 to ‘vandalisation’.

  16. A recent study using DPR data estimated 3.1 million barrels spilled between 1976 and 2014. See Enegide, C. and Chukwuma K, C. 2018. Oil Spillage and Heavy Metals Toxicity Risk in the Niger Delta, Nigeria. Journal of health & pollution, 8, pp. 1-8.

  17. A 2006 UNDP report states that there has been a total of 6,817 oil spills between 1976 and 2001, which account for a loss of three million barrels of oil of which more than 70 percent was not recovered. Two-thirds of these spills occurred off-shore, a figure which seems implausible. See UNDP (United Nations Development Programme). 2018. National Human Development Report 2018: Nigeria. New York.

  18. Department of Petroleum Resources. 2019. 2018 Nigerian oil and gas industry annual report. [Accessed 3 October 2021]. Available at https://www.nuprc.gov.ng/w...

  19. Amnesty International. 2013. Bad Information: Oil Spill Investigations in the Niger Delta. London: Amnesty International Publications [Online]. [Accessed 24 April 2021]. Available at https://www.amnestyusa.or...

  20. Amnesty International. 2018. Negligence in the Niger Delta: Decoding Shell and Eni's poor records on oil spills. Amnesty International [Online]. [Accessed 30 January 2022]. Available at https://www.amnesty.org/en/...

  21. Amnesty International. 2015. Long-awaited victory: Shell to pay out $83 million over Nigeria Delta oil spills. [Online]. [Accessed 29 September 2020]. Available at https://www.amnesty.org.uk...

  1. Amnesty International. 2009. Nigeria: Petroleum pollution and poverty in the Niger Delta. Amnesty International [Online]. Available at https://www.amnesty.org/en/...

  2. 546 million gallons, cited in Francis, P., Lapin, D. and Rossiasco, P. 2021. Securing Development and Peace in the Niger Delta: A Social and Conflict Analysis for Change. USA: Woodrow Wilson International Center for Scholars.

  3. Kadafa, A. A. 2012. Environmental Impacts of Oil Exploration and Exploitation in the Niger Delta of Nigeria. Global Journal of Science, Frontier Research, 12(3) - cites 9 - 13 billion barrels over last 50 years.

  4. Palinkas, L., Downs, M., Petterson, J. and Russell, J. 1993. Social, cultural, and psychological impacts of the Exxon Valdez oil spill. Human Organization, 52(1), pp.1-13. [Accessed 24 Apr. 2021]. Available at https://www.jstor.org/sta...

  5. Amnesty International. 2018. Negligence in the Niger Delta: Decoding Shell and Eni's poor records on oil spills. Amnesty International [Online]. [Accessed 30 January 2022]. Available at https://www.amnesty.org/en/...

  6. Global Oil Infrastructure Tracker. Global Energy Monitor. June 2022 release.

  7. Amnesty International. 2018. Negligence in the Niger Delta: Decoding Shell and Eni's poor records on oil spills. Amnesty International [Online]. [Accessed 30 January 2022]. Available at https://www.amnesty.org/en/... See also Amnesty International. 2009. Nigeria: Petroleum pollution and poverty in the Niger Delta. Amnesty International [Online]. Available at https://www.amnesty.org/en/... Watts, M. and Zalik, A. 2020. Consistently unreliable: Oil spill data and transparency discourse. The Extractive Industries and Society, 7, pp. 790-795. Calculation based on data from NOSDRA. n.d. Nigerian Oil Spill Monitor. [Accessed 11 July 2021]. Available at https://nosdra.oilspi...

  8. NOSDRA. n.d. Nigerian Oil Spill Monitor. [Accessed 3 October 2021]. Available at https://nosdra.oilspi...

  9. Independent research conducted by the BSOEC suggests that Nembe and Brass also consistently rank amongst the highly affected LGAs, by oil pollution of different kinds, notably effluent waste (Brass Canal).

  10. NOSDRA. n.d. Nigerian Oil Spill Monitor. [Accessed 3 October 2021]. Available at https://nosdra.oilspi... Database of Global Administrative Areas (GADM) 2018. GADM Data. [Accessed 3 October 2021]. Available at https://gadm.org/data...

  11. Bayelsa State Oil and Environment Commission. 2019. Oral evidence submitted as evidence at the BSOEC hearings, Nembe, 10 July 2019.

  12. Bayelsa State Oil and Environment Commission. 2019. Oral evidence submitted as evidence at the BSOEC hearings, Southern Ijaw, 11 July 2019.

  13. World Bank. n.d. Gas Flaring Explained. [Accessed at 15 November 2022]. Available at https://www.worldbank.org...

  14. Ezenwaji, E. E., Okoye, A. C. and Otti, V. I. 2013. Effects of gas flaring on rainwater quality in Bayelsa State, Eastern Niger-Delta region, Nigeria. Journal of Toxicology and Environmental Health Sciences, 5, pp. 97-105.

  15. World Bank. n.d. Global Gas Flaring Data. Available at https://www.worldbank.org...

  16. Atevure, B. S. V. 2004. Processes of Oil Production and Environmental Degradation: An Overview. Journal of Environmental Analysis, 2(1), pp. 76-85.

  17. World Bank. n.d. Global Gas Flaring Data. Available at https://www.worldbank.org... NNPC has its own flare data which suggests substantially lower flare volumes especially between 2017 and 2021 (see https://nosdra.gasflaret...) Both sources, however, indicate an uneven but downward trend in flare volumes over the last decade.

  18. NOSDRA holds flaring data (see https://nosdra.gasflaretr...) which is sometimes inconsistent with the GGFR data: according to NOSDRA, the 2021 figure for CO2 emissions was 14 million tons (substantially less than GGFR’s estimates) and gas flare volumes 260 million Mscf (7.3 million cubic metres), more than 10 percent larger than GGFR figures.

  19. Jack, J. 2017. Gas Flaring Health Impacts and Conflict Potentials in the Niger Delta. Stakeholder Democracy Network.

  20. Ezenwaji, E. E., Okoye, A. C. and Otti, V. I. 2013. Effects of gas flaring on rainwater quality in Bayelsa State, Eastern Niger-Delta region, Nigeria. Journal of Toxicology and Environmental Health Sciences, 5, pp. 97-105.

  21. The disparity in flare volumes between GGFR and NOSDRA is, in part, a reflection of the number of flare sites selected and whether flares discharging relatively small volumes are included.

  22. Schick, L., Myles, P. and Okelum, O. E. 2018. Gas flaring continues scorching Niger Delta. DW [Online]. 14 November. [Accessed 30 August 2021]. Available at https://www.dw.com/en/gas...

  23. Donwa, P. A., Mgbame, C. O. and Utomwen, O. A. 2015. Gas flaring in the oil and gas sector in Nigeria. Gas. International Journal of Commerce and Management Research, 1, pp. 28-39.

  24. Gobo, A. E., Richard, G. and Ubong, I. U. 2009. Health impact of gas flares on Igwuruta/ Umuechem communities in River State. Applied Sciences and Environmental Management, 13, pp. 27-33. See also Maduka, O. and Tobin-West, C. 2017. Is living in a gas-flaring host community associated with being hypertensive? Evidence from the Niger Delta region of Nigeria. BMJ Global Health, 2, pp. 1-8.

  25. Angiamowei, S. V., Nwankwor, C. A. and Ahiarakwem, G. I. 2019. Assessment of air quality around Gbaran–Ubie gas processing plant, Yenagoa, Bayelsa State, Southern Nigeria. Journal of Environment and Earth Science, 9, pp. 11-18.

  26. Saint, E. 2022. “It chokes me”: A black soot nightmare in the Niger Delta. Fair Planet [Online]. 10 January. [Accessed 14 November 2022]. Available at https://www.fairplanet.org...

  27. Saint, E. 2022. “It chokes me”: A black soot nightmare in the Niger Delta. Fair Planet [Online]. 10 January. [Accessed 14 November 2022]. Available at https://www.fairplanet.org...

  28. Aigberua, A. and Tarawou, T. 2019. Water Quality Index (WQI) assessment along inland fresh waters of Taylor Creek in Bayelsa State, Nigeria. Journal of Environmental Treatment Techniques, 7, pp. 260 269.

  29. Atuma, M. I. and Ojeh, V. N. 2013. Effect of gas flaring on soil and cassava productivity in Ebedei, Ukwuani Local Government Area, Delta State, Nigeria. Journal of Environmental Protection, 4, pp. 1054-1066. See also Ajugwo, A. O. 2013. Negative effects of gas flaring: The Nigerian experience. Journal of Environment Pollution and Human Health, 1, pp. 6-8.

  30. Ubani, E. and Onyejekwe, I. 2013. Environmental impact analyses of gas flaring in the Niger delta region of Nigeria.American journal of scientific and industrial research, 4, pp. 246-252.

  31. Oyadongha, S. 2021. Nigeria: Overflowing Gas Flare in Ogboinbiri - Bayelsa Villagers Trigger Alarm Over Quaking, Cracking Homes. 9 March. [Accessed 23 December 2022]. Available at https://www.vanguardngr.com...

  32. Angiamowei, S. V., Nwankwor, C. A. and Ahiarakwem, G. I. 2019. Assessment of air quality around Gbaran–Ubie gas processing plant, Yenagoa, Bayelsa State, Southern Nigeria. Journal of Environment and Earth Science, 9, pp. 11-18.

  1. David, A. E., Kesiye, I. A., Stephen, U. A., Nimibofa, A. and Etta, B. A. 2017. Measurement of Total Suspended Particulate Matter (TSP) in an Urban Environment: Yenagoa and Its Environs. Geography, Environment and Earth Science International, 11, pp. 1-8.

  2. Angiamowei, S. V., Nwankwor, C. A. and Ahiarakwem, G. I. 2019. Assessment of air quality around Gbaran–Ubie gas processing plant, Yenagoa, Bayelsa State, Southern Nigeria. Journal of Environment and Earth Science, 9, pp. 11-18.

  3. Angiamowei, S. V., Nwankwor, C. A. and Ahiarakwem, G. I. 2019. Assessment of air quality around Gbaran–Ubie gas processing plant, Yenagoa, Bayelsa State, Southern Nigeria. Journal of Environment and Earth Science, 9, pp. 11-18.

  4. Angiamowei, S. V., Nwankwor, C. A. and Ahiarakwem, G. I. 2019. Assessment of air quality around Gbaran–Ubie gas processing plant, Yenagoa, Bayelsa State, Southern Nigeria. Journal of Environment and Earth Science, 9, pp. 11-18.

  5. NOSDRA. n.d. Nigerian Gas Flare Tracker [Online]. [Accessed 3 October 2021]. Available at https://nosdra.gasflaretr...

  6. Oyadongha, S. 2017. Bayelsa monarch bemoans the effect of toxic waste dump. Vanguard [Online]. 9 February. [Accessed 3 October 2021]. Available at https://www.vanguardngr.com.... See also Mirinn, E., Berezi, E. P. and Nwauche, K. T. 2020. Effect of Drilling Wastes on Urease Activities and Substrate Induced Respiration (SIR) in Wetland Soil of Delta and Bayelsa States, South-South, Nigeria. Chemical Science International Journal, 29(2), pp. 34-47. [Accessed 3 October 2021]. Available at https://doi.org/10.9734/C...

  7. Stakeholder Democracy Network (SDN). 2015. Communities not Criminals: Illegal oil refining in the Niger Delta. [Accessed 3 October 2021]. Available at https://www.stakeholderde... See also Stakeholder Democracy Network. 2018. More money, more problems: Economic dynamics of the artisanal oil industry in the Niger Delta over five years. [Accessed 3 October 2021]. Available at https://www.stakeholderde...

  8. Stakeholder Democracy Network. 2015. Communities Not Criminals: Illegal Oil Refining in the Niger Delta. [Accessed 3 October 2021]. Available at https://www.stakeholderde... Udoma, M. 2023. JTF destroys 1,800 illegal refineries, arrests 699 suspects in 2022. Sweet Crude Reports [Online]. 1 January. Accessed 5 March 2023. Available at https://sweetcrudereports... Yusuf, K. 2022. Analysis: How broke Nigeria lost $10 billion to crude oil theft in seven months. Premium Times Nigeria [Online]. 8 September. Accessed 5 March 2023. Available at https://www.premiumtimesng... Okungbowa, A. O. 2022. Crude Oil Theft: Whither Nigeria?. This Day [Online]. Accessed 5 March 2023. Available at https://www.thisdaylive.com...

  9. Von Kemedi, D. 2005. Oil on Troubled Water. Working Paper [Online]. Institute of International Studies. Available at https://geography.berkeley.edu/sites/default/files/5-vonkemedi.pdf

  10. HRH Godfrey Isolo, Amanyanabo elect.

  11. They include Shell, Chevron, ExxonMobil etc.

  12. Allen, F. 2015. Shell Divestment and Local Communities Responses in the Niger Delta. Environmental Rights Action (ERA)

  13. Seeking Alpha. 2015. Ben van Beurden on Q1 2015 Results – Earnings Call Transcript [Online]. [Accessed 27 April 2023]. Available at https://seekingalpha.com/article...

  14. Historical spills are actually more difficult to address due to the age of the impacted site and in some cases they may require special remediation procedures such as salt or produce water and hydrocarbons (emulsion) mixture and old pits, see R.34 of the Clean-up Regulations.

  15. Jamieson, A and Gomes, S. 2020. An Independent Forensic Assessment of Environmental Pollution in Bayelsa State. Bayelsa State Oil and Environmental Commission. For reference to international minimum standards including biodiversity and associated biophysical and social parameters, see IUCN. 2013. Sustainable Remediation and Rehabilitation of Biodiversity and Habitats of Oil Spill Sites in the Niger Delta. A similar study in the Imiringi town that hosts the Kolo Creek oil and gas fields was presented in this report.

  16. Jamieson, A and Gomes, S. 2020. An Independent Forensic Assessment of Environmental Pollution in Bayelsa State. Bayelsa State Oil and Environmental Commission.

  17. Jamieson, A and Gomes, S. 2020. An Independent Forensic Assessment of Environmental Pollution in Bayelsa State. Bayelsa State Oil and Environmental Commission. For reference to international minimum standards including biodiversity and associated biophysical and social parameters, see IUCN. 2013. Sustainable Remediation and Rehabilitation of Biodiversity and Habitats of Oil Spill Sites in the Niger Delta. A similar study in the Imiringi town that hosts the Kolo Creek oil and gas fields was presented in this report.

  18. Jamieson, A and Gomes, S. 2020. An Independent Forensic Assessment of Environmental Pollution in Bayelsa State. Bayelsa State Oil and Environmental Commission.

  19. IUCN Niger-Delta Panel. 2013. Sustainable remediation and rehabilitation of biodiversity and habitats of oil spill sites in the Niger Delta: Annex Ig. Nembe (Ogbolomabiri): Biophysical Report. IUCN: Gland. pp. 1-70.

  20. Jamieson, A and Gomes, S. 2020. An Independent Forensic Assessment of Environmental Pollution in Bayelsa State. Bayelsa State Oil and Environmental Commission.

  21. Jamieson, A and Gomes, S. 2020. An Independent Forensic Assessment of Environmental Pollution in Bayelsa State. Bayelsa State Oil and Environmental Commission.

  22. World Health Organization, International Atomic Energy Agency & Food and Agriculture Organization of the United Nations. 1996. Trace elements in human nutrition and health. World Health Organization. Available at https://apps.who.int/iris/handle/10665/37931. 1996, OYEYEMI et al. n/a 'Health impact of oil spills and gas flaring in Bayelsa. (Oasis Public Health Consulting Ltd in collaboration with Oil Pollution Research Group (Niger Delta University). A research report commissioned by the Bayelsa State Oil and Environmental Commission (unpublished), p. 55.

  23. Jamieson, A and Gomes, S. 2020. An Independent Forensic Assessment of Environmental Pollution in Bayelsa State. Bayelsa State Oil and Environmental Commission. University Of California San Francisco Health (UCSF Health). 2019. Medical Tests: Lead levels - blood [Online]. [Accessed 3 October 2020]. Available at https://www.ucsfhealth.org/medical-tests/lead-levels---blood. Dugdale, D. C. and Zieve, D. April 26, 2019. Chromium-blood test [Online]. MedlinePlus. [Accessed 3 October 2020]. Available at https://medlineplus.gov/ency/article/003359.htm.

  24. Angiamowei, S. V., Nwankwor, C. A. and Ahiarakwem, G. I. 2019. Assessment of air quality around Gbaran–Ubie gas processing plant, Yenagoa, Bayelsa State, Southern Nigeria. Journal of Environment and Earth Science, 9, pp. 11-18.

  25. World Health Organisation, ‘Trace Elements in Human Nutrition and Health’, 1996 OYEYEMI et al. n/a ‘Health impact of oil spills and gas flaring in Bayelsa. (Oasis Public Health Consulting Ltd in collaboration with Oil Pollution Research Group (Niger Delta University). A research report commissioned by the Bayelsa State Oil and Environmental Commission (unpublished), p. 55.

  1. World Health Organisation, ‘Trace Elements in Human Nutrition and Health’, 1996 OYEYEMI et al. n/a ‘Health impact of oil spills and gas flaring in Bayelsa. (Oasis Public Health Consulting Ltd in collaboration with Oil Pollution Research Group (Niger Delta University). A research report commissioned by the Bayelsa State Oil and Environmental Commission (unpublished), p. 55.

  2. Oyeyemi et al. n/a ‘Health impact of oil spills and gas flaring in Bayelsa. (Oasis Public Health Consulting Ltd in collaboration with Oil Pollution Research Group (Niger Delta University). A research report commissioned by the Bayelsa State Oil and Environmental Commission (unpublished).

  3. Gobo, A. E., Richard, G and Ubong, I. U. 2009. Health impact of gas flares on Igwuruta / Umuechem communities in Rivers State. Journal of Applied Sciences and Environmental Management, 13(3), pp. 27-33.

  4. Numbere, A. O. 2018. Mangrove species distribution and composition, adaptive strategies and ecosystem services in the Niger River Delta, Nigeria. In Mangrove and Ecosystem Ecology and Function, S. Sharma, ed. IntechOpen. pp. 17-39. Available at https://www.intechopen.com/chapters/62582.

  5. A more conservative 2003 figure of 10 percent mangrove loss in Nigeria due to oil is cited in IUCN Niger Delta Panel. 2018. Developing a biodiversity conservation strategy for the Niger Delta: Integrating biodiversity considerations into SPDC’s operation. Gland, Switzerland: IUCN. See also Obot, E. A., Ezealor, A., King, R., Bassey, A. and Eniang, E. A. 2003. A new Barn Swallow (Hirundo rustica) Roost at Itu Wetlands Akwa Ibom State, Nigeria. Roan, 1(1/2), pp. 103– 118.

  6. Langeveld, J. W.A. and S. Delany. 2014. The impact of oil exploration, extraction and transportation on mangrove vegetation and carbon stock in Nigeria 1401. Biomass Research Report, 1401: Biomass Research, Wageningen. James, G. K., Adegoke, J. O., Osagie, S., Ekechukwu, S., Nwilo, P. and Akinyede, J. 2013. Social valuation of mangroves in the Niger Delta region of Nigeria. International Journal of Biodiversity Science, Ecosystem Services & Management, 9, pp. 311-323 - notes that 40 percent of the mangrove vegetation in the Niger Delta has died since the commercial production of oil began in 1958. An estimated 80 percent of this mangrove vegetation is distributed across just three states – Bayelsa, Delta and River – together totalling an area of 9,763.9 km2 of mangroves, of which 3,533.5 km2 (36.2 percent) is in Bayelsa State. This implies that, based on the overall mortality rate of 40 percent, 1,413.4 km2 of the mangrove vegetation in Bayelsa have died since oil production commenced in 1958.

  7. Duke, N. 2016. Oil spill impacts on mangroves: Recommendations for operational planning and action based on a global review. Marine Pollution Bulletin, 109, pp. 700-715. For discussion of artisanal refining in Bodo (Rivers State) and its role in mangrove destruction see Gundlach, E. R. 2018. Oil-related mangrove loss east of Bonny River, Nigeria. In: Makowski, C. and Finkl, C. (eds) Threats to Mangrove Forests. Coastal Research Library, 25, Springer Nature 2018, pp. 267-321. [Accessed 3 October 2021]. Available at https://doi.org/10.1007/978-3-319-73016-5_13. Little D. I. 2018. Mangrove restoration and mitigation after oil spills and development projects in East Africa and the Middle East. In: Makowski, C. and Finkl C. (eds) Threats to Mangrove Forests. Coastal Research Library, 25, Springer Nature 2018, pp. 637-698. [Accessed 3 October 2021]. Available at https://doi.org/10.1007/978-3-319-73016-5_30.

  8. Ohimain, E. 2004. Environmental impacts of dredging in the Niger Delta; Options for sediment relocation that will mitigate acidification and enhance natural mangrove restoration. Terra et Aqua, 97: pp. 1-19.

  9. Adekola, O and Mitchell, G. 2011. The Niger Delta wetlands: threats to ecosystem services, their importance to dependent communities and possible management measures. International Journal of Biodiversity Science, Ecosystem Services & Management, 7(1), pp. 50–68.

  10. Cole, L. E. S., Bhagwat, S. A. and Willis, K. J. 2014. Recovery and resilience of tropical forests after disturbance. Nature Communications, 5, 3906. [Accessed 3 October 2013]. Available at https://www.nature.com/articles/ncomms4906.

  11. Onyena, A. M. and Sam, K. 2020. A review of the threat of oil exploitation to the mangrove ecosystem: Insights from Niger Delta, Nigeria. Global Ecology and Conservation, 22, e0096, pp. 1-12.

  12. Atoufi, H. D. and Lampert, D. J. 2020. Impacts of oil and gas production on contaminant levels in sediments. Current Pollution Reports 6, pp. 43–53.

  13. Bayelsa State Oil and Environment Commission. 2019. Oral testimony submitted as evidence at the BSOEC hearings, Twon Brass, 10 July 2019.

  14. Bayelsa State Oil and Environment Commission. 2019. Oral testimony submitted as evidence at the BSOEC hearings, Twon Brass, 10 July 2019.

  15. Bayelsa State Oil and Environment Commission. 2019. Oral testimony submitted as evidence at the BSOEC hearings, Twon Brass, 10 July 2019.

  16. Shell. [No date]. Spill incident data. [Online]. [Accessed 24 September 2022]. Available at https://www.shell.com.ng/sustainability/environment/oil-spills/spill-incident-data.html.

  17. IUCN Niger-Delta Panel. 2013. Sustainable remediation and rehabilitation of biodiversity and habitats of oil spill sites in the Niger Delta: Annex Ig. Nembe (Ogbolomabiri): Biophysical Report. IUCN: Gland. pp. 1-70 and Luiselli, L. and Akani, G. C. 2003. An indirect assessment of the effects of oil pollution on the diversity and functioning of turtle communities in the Niger Delta, Nigeria. Animal Biodiversity and Conservation 26(1), pp. 57-65.

  18. Pegg, S and Zabbey, N. 2013. Oil and Water: The Bodo Spills and the Destruction of Traditional Livelihood Structures in the Niger Delta, Community Development Journal, 48(3), pp. 391–405.

  19. Pegg, S and Zabbey, N. 2013. Oil and Water: The Bodo Spills and the Destruction of Traditional Livelihood Structures in the Niger Delta, Community Development Journal, 48(3), pp. 391–405.

  20. Bebeteidoh, O. L., Kometa, S., Pazouki, K. and Norman, R. 2020. Sustained impact of the activities of local crude oil refiners on their host communities in Nigeria. Heliyon 6(6), e04000.

  21. Bebeteidoh, O. L., Kometa, S., Pazouki, K. and Norman, R. 2020. Sustained impact of the activities of local crude oil refiners on their host communities in Nigeria. Heliyon 6(6), e04000.

  22. United Nations Environment Programme (UNEP). 2011. Environmental Assessment of Ogoniland. Nairobi: United Nations Environment Programme. [Accessed 3 October 2021]. Available at https://www.unep.org/explore-topics....

  23. Ipingbemi, O. 2009. Socio-economic implications and environmental effects of oil spillage in some communities in the Niger delta. Journal of Integrative Environmental Sciences,6, pp. 7-23..

  24. Ebere, N. M, Onoja, A. O. and Monsi, B. 2016. A comparative analysis of productivities in shellfish collection in oil spill and non-oil spill communities of River State, Nigeria. Consilience, 15, pp. 34-49.

  25. Pegg, S and Zabbey, N. 2013. Oil and Water: The Bodo Spills and the Destruction of Traditional Livelihood Structures in the Niger Delta, Community Development Journal, 48(3), pp. 391–405.

  26. Esu, B. and Dominic, O. 2013. Perceived effects of gas flaring 7on socio-economic well-being of farming households in Ogbia Local Government Area, Bayelsa State. American Journal of Research Communication, 1(3), pp. 27-34.

  27. Ibegu, K. A. and Olusola, A. M. 2017. Effects of Oil Operations on Epebu Community in Bayelsa State. Covenant Journal of Research in the Built Environment, 5(2). Available at https://journals.covenantuniversity.edu.....

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  14. Bayelsa State Oil and Environment Commission. 2019. Correspondence submitted to the Commission relating to the Twon Brass kingdom.

  15. Bayelsa State Oil and Environment Commission. 2019. Testimony submitted as evidence at the BSOEC hearings, Nembe, 24 May 2019.

  16. Dakokolo, B. HRM. 2021. The Riddle of the Oil Theft. Nigeria: Purple Shelves Ltd. Testimonies, pp. 404 - 412: “Within weeks of being around, they (IOCs) completely disorganised the social equilibrium the community had enjoyed for so long. Their workers could not restrain their libido and started committing all kinds of sexual atrocities, using their superior financial advantage... After barely four months of their stay, calamity was wreaked upon the community. It was discovered that a lot of underage girls had been impregnated by oil workers who sneaked into the community at night to lure vulnerable young girls to their love nests”. Testimonies noted that staff of the IOCs ‘wooed’ ladies from the local communities with financial resources and dehumanised some of the women in the process. One of the respondents noted that “They call our mothers, sisters, daughters and even our wives the most derogatory nickname, ‘bush-meat', meaning a game animal. Without any sense of guilt, they call these names to our very faces... I have never felt more insulted than this as a personfrom an oil-bearing and facilities hosting community”..

  17. Human Rights Watch. 1999. The Destruction of Odi and Rape in Choba [Online]. [Accessed 5 February 2022]. Available at https://www.hrw.org/legacy/press/1999/....

  18. The Eagle Online. 2018. NAPTIP to rescue Nigerian victims of human trafficking, others around West Africa. The Eagle Online. 4 May. [Accessed 19 October 2022]. Available at https://theeagleonline.com.ng/.../.

  19. Aghalino, S.O. 2000. Petroleum exploitation and the agitation for compensation by oil producing communities in Nigeria. Geo Studies Forum, 1(1&2), pp. 11-20.

  20. See also Dakolo, B. HRM. 2021. The Riddle of the Oil Thief. Nigeria: Purple Shelves Ltd.

  21. Dakolo, B. HRM. 2021. The Riddle of the Oil Thief. Nigeria: Purple Shelves Ltd.

  22. Bayelsa State Oil and Environment Commission. 2019. Oral testimony submitted as evidence at the BSOEC hearings, Yenagoa, 9 July 2019.

  23. Amnesty International, Environmental Rights Action/ Friends of the Earth, Nigeria, and Friends of the Earth Europe Milieudefensie/ Friends of the Earth. 2020. No Clean-up, No Justice: An Evaluation of the Implementation of UNEP’s Environmental Assessment of Ogoniland, Nine Years On. [Accessed 3 October 2021]. Available at https://www.amnesty.org/en...

  24. Bayelsa State Oil and Environmental Commission. 2019. Oral testimony submitted as evidence at the BSOEC hearings, Ekeremor, 11 July 2019.

  25. Thomas, C. C., Nsonwu-Anyanwu, A. C., Usoro, C. A., Eni-Yimini, S. A. and Idenyi, A. N. 2021. Hepato-renal toxicities associated with heavy metal contamination of water sources among residents of an oil contaminated area in Nigeria. Ecotoxicology and Environmental Safety, 212, 11198, p.1-7. [Accessed 3 October 2021]. Available at https://doi.org/10.1016/j...

  26. Environmental Rights Action (ERA) and Friends of The Earth, Nigeria. 2015. Fresh Oil Spill along Agip’s Tebidaba/ Ogboinbiri pipeline at Ikebiri. Field Report #370.

  27. Environmental Rights Action (ERA) and Friends of The Earth, Nigeria. 2017. Massive Oil Spill from AGIP’s Clough Creek.

  28. National Bureau of Statistics. 2019. 2018 Statistical Report on Women and Men in Nigeria. National Bureau of Statistics: Nigeria.

  29. National Population Commission - NPC/Nigeria and ICF. 2019. Nigeria Demographic and Health Survey 2018. Abuja, Nigeria, and Rockville, Maryland, USA: NPC and ICF.

  30. National Population Commission - NPC/Nigeria and ICF. 2019. Nigeria Demographic and Health Survey 2018. Abuja, Nigeria, and Rockville, Maryland, USA: NPC and ICF.

  31. Bruederle, A. and Hodler, R. 2019. Effect of oil spills on infant mortality in Nigeria. Proceedings of the National Academy of Sciences of the United States of America, pp. 116, 5467-5471.

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  2. McFubara, K. G., Edoni, E. R. and Ezonbodor-Akwagbe, R.E. 2012. Health manpower development in Bayelsa State, Nigeria. Risk Management and Healthcare Policy, 5, pp. 127-135.

  3. David, A. E., Kesiye, I. A., Stephen, U. A., Nimibofa, A. and Etta, B. A. 2017. Measurement of Total Suspended Particulate Matter (TSP) in an Urban Environment: Yenagoa and Its Environs. Geography, Environment and Earth Science International, 11, pp. 1-8.

  4. Angiamowei, S. V., Nwankwor, C. A. and Ahiarakwem, G. I. 2019. Assessment of air quality around Gbaran–Ubie gas processing plant, Yenagoa, Bayelsa State, Southern Nigeria. Journal of Environment and Earth Science, 9, pp. 11-18.

  5. Angiamowei, S. V., Nwankwor, C. A. and Ahiarakwem, G. I. 2019. Assessment of air quality around Gbaran–Ubie gas processing plant, Yenagoa, Bayelsa State, Southern Nigeria. Journal of Environment and Earth Science, 9, pp. 11-18.

  6. Angiamowei, S. V., Nwankwor, C. A. and Ahiarakwem, G. I. 2019. Assessment of air quality around Gbaran–Ubie gas processing plant, Yenagoa, Bayelsa State, Southern Nigeria. Journal of Environment and Earth Science, 9, pp. 11-18.

  7. Angiamowei, S. V., Nwankwor, C. A. and Ahiarakwem, G. I. 2019. Assessment of air quality around Gbaran–Ubie gas processing plant, Yenagoa, Bayelsa State, Southern Nigeria. Journal of Environment and Earth Science, 9, pp. 11-18; David, A. E., Kesiye, I. A., Stephen, U. A., Nimibofa, A. and Etta, B. A. 2017. Measurement of Total Suspended Particulate Matter (TSP) in an Urban Environment: Yenagoa and Its Environs. Geography, Environment and Earth Science International, 11, pp. 1-8.

  8. Pilkington, E. 2009. Shell pays out $15.5m over Saro-Wiwa killing. The Guardian [Online]. 9 June. [Accessed 9 April 2023]. Available at https://www.theguardian.com/world...


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