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International Journal of
eISSN: 2576-4454

Hydrology

Research Article Volume 8 Issue 6

Unveiling the impact: gas flaring on artisanal fisheries in Taylor creek, Bayelsa state, Nigeria

Kwen Keme- Iderikumo,1 Eli Akayinaboderi Augustus,2 Morufu Olalekan Raimi2,3

1Department of Research Operations, National Institute for Freshwater Fisheries Research, New Bussa, Niger State, Nigeria
2Department of Environmental Management and Toxicology, Faculty of Sciences, Federal University Otuoke, Bayelsa State, Nigeria
3United Nations Economic Commission for Europe (UNECE) Expert Group on Resources Management (EGRM) on the Draft United Nations Framework Classification for Resources (UNFC) Supplemental Specifications for Groundwater Resources, Geneva, Switzerland

Correspondence: Morufu Olalekan Raimi, Environmental Management and Toxicology, Federal University Otuoke, Nigeria, Tel +2347038053786

Received: November 20, 2024 | Published: December 31, 2024

Citation: Keme-Iderikumo K, Augustus EA, Raimi MO. Unveiling the impact: gas flaring on artisanal fisheries in Taylor creek, Bayelsa state, Nigeria. Int J Hydro. 2024;8(6):235-248. DOI: 10.15406/ijh.2024.08.00395

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Abstract

Rationale: Gas flaring is a significant environmental concern in many regions, including the downstream area of Taylor Creek, Bayelsa State, Nigeria. Its impact on artisanal fisheries, a vital economic activity in the area, warrants investigation to understand the extent of its effects.

Objectives: This study aimed to assess the effects of gas flaring on artisanal fisheries in the downstream area of Taylor Creek, Bayelsa State, Nigeria, from August 2023 to January 2024.

Methods: Structured questionnaires were utilized in a descriptive survey research design to collect data during the specified period.

Results: The study found that gas flaring profoundly affects artisanal fisheries activities in the area. These effects include a drastic reduction in fish catch, extinction of certain fish species, increased fish prices, indiscriminate fish mortality, disrupted fishing schedules, altered water body dynamics, impaired spawning activities, fish migration, and economic hardships for fishers. Additionally, gas flaring contributes to fish size reduction, abandonment of the fishing sector by artisanal fishers, increased time spent on fishing, and accelerated degradation of fishing implements.

Conclusion: Gas flaring negatively impacts artisanal fisheries in the downstream area of Taylor Creek, Bayelsa State, Nigeria. Urgent measures are necessary to mitigate these effects and preserve the local ecosystem.

Recommendation: To address these issues, it is recommended that gas flaring be utilized for beneficial purposes such as gas injection or electricity generation. Government intervention is needed to restore extraction areas, and companies must adopt safe and environmentally friendly operations to prevent further environmental degradation. Additionally, new legislation should be enacted to protect the environment and control pollution caused by gas flaring in the study area. These measures are essential for safeguarding the environment and sustaining artisanal fisheries in the region.

Keywords: artisanal fisheries, effects, gas flaring, Taylor creek, core Niger delta, Nigeria

Introduction

Gas flaring, a common practice in oil-producing regions, involves the burning of natural gas mixed with crude oil during extraction and processing. Initially considered a precautionary measure during breakdowns or emergencies, it has evolved into a routine disposal method for excess gas. The process is often necessitated by the difficulty in separating associated gas from crude oil, leading to its combustion either directly from pits or through flare stacks. However, gas flares emit a range of pollutants, including nitrogen oxides, sulfur dioxide, ammonia, methane, carbon dioxide, and carcinogenic substances like benzene, toluene, xylene and hydrogen sulfide (Raimi et al., 2020; Raimi et al., 2021).1–10 In Nigeria, particularly in the Niger Delta Area, gas flaring has become a significant issue due to the operations of multinational oil companies such as Shell Petroleum Development Company (SPDC) and Agip. Despite Nigeria's substantial gas reserves, it ranks among the top countries globally for gas flaring, with approximately 16% of associated gas being flared annually. This practice not only wastes valuable energy resources but also contributes to environmental degradation and health hazards, affecting both the local ecosystem and human populations (Olalekan et al., 2022; Stephen et al., 2023).11–25

The Niger Delta Area, encompassing several states and serving as the economic hub of Nigeria due to its abundant oil reserves, bears the brunt of these impacts. Despite its economic importance, the region faces neglect from oil companies in prioritizing environmental and human health concerns associated with gas flaring. Regulatory bodies like the Federal Environmental Protection Agency (FEPA) and the Department of Petroleum Resources (DPR) have failed to implement effective anti-gas flaring policies or monitor emissions adequately (Raimi et al., 2020).26–32 The core Niger Delta, covering approximately 70,000 square kilometers and comprising Bayelsa, Delta, and Rivers States, serves as Nigeria's economic nerve center owing to its immense oil reserves. Despite its relatively small landmass compared to other oil-producing regions globally, such as Saudi Arabia's Eastern Province, Siberia in Russia, Texas in the United States, or Venezuela's Orinoco Belt, the Niger Delta plays a crucial role in Nigeria's economy. Similar to these regions, the Niger Delta's oil industry significantly contributes to government revenue, GDP, and overall economic growth. However, its economic importance is notably concentrated within Nigeria, where it remains a primary driver of the country's energy sector and a key player in the global oil market (Olalekan et al., 2019).33

However, in 2000 the government of the Federation Republic of Nigeria included Abia, Akwa Ibom, Cross River, Edo, Imo and Ondo States in the region.34 Obi et al.21 reported that gas flaring has being responsible for several health and environmental challenges and some of the adverse effects of gas flaring include climate change,35,36 environmental pollution,37–44 global warming, loss of lives and respiratory problems (Raimi et al., 2020).45,7,9 The effects of gas flaring on fishery refers to the influence of burning natural gas that is often released during oil extraction on aquatic ecosystems, particularly on fish populations (Ayibatonye et al., 2024a, b).43,44 Gas flaring emits various pollutants, including greenhouse gases, which can affect the groundwater quality (Raimi et al., 2021b; Raimi et al., 2023),45–58 habitat, and overall health of the aquatic environments.59–65 According to Okonkwo66 gas flaring which the practice of burning off excess natural gas during oil extraction and processing, has turn out to be a substantial environmental concern in many oil-producing regions round the world (https://earthjournalism.net/stories/gas-flaring-in-the-niger-delta-harming-health-climate-and-environment).

While, the downstream region of Taylor Creek emerges as a pivotal hub for fisheries activities within Bayelsa State, Nigeria. Renowned for its abundant aquatic biodiversity teeming with diverse fish species, crustaceans, and mollusks, this area holds significant importance. The fisheries operations here are not merely economic ventures; they embody a lifeline for local communities, fostering livelihoods by serving as crucial sources of income and nutrition. This symbiotic relationship between the fisheries and the communities underscores the pivotal role played by Taylor Creek's downstream area in sustaining the socio-economic fabric of the region (Ayibatonye et al., 2024a, b; Kwen et al., 2019). The fish species are essential for local diet and are also commercially important to the inhabitants of the down-stream area of Taylor Creek. While, the impact of gas flaring on artisanal fisheries has not been adequately studied, despite its critical importance to local livelihoods and aquatic ecosystems. The environmental and health impacts of gas flaring are well-documented, specific effects on fisheries particularly artisanal fisheries in oil-producing regions like the Niger Delta remain underexplored. Gas flaring alters water quality, temperature, and oxygen levels, affecting fish populations and aquatic biodiversity. Furthermore, pollutants such as heavy metals and polycyclic aromatic hydrocarbons bioaccumulate in fish, posing significant health risks to consumers. In the downstream region of Taylor Creek, Bayelsa State, where fisheries provide both sustenance and income for local communities, this gap in knowledge limits the development of targeted policies to address these impacts.

Given the socio-economic reliance on fisheries in this region, research is urgently needed to inform sustainable environmental preservation and fisheries management strategies. The effects of gas flaring on the environment are well-documented and have been studied in various contexts, such as air quality,68,7,9 health impacts (Sarah et al., 2024)69,27,29–31 and aquatic pollution.70 However, its specific effects on local ecosystems, particularly fisheries in the down-stream area of Taylor Creek, Bayelsa State, Nigeria, has received limited or no attention (Ayibatonye et al., 2024a, b).43,44 The down-stream area of Taylor Creek is a vital ecosystem for the local communities, providing a source of livelihood through fisheries. This area is situated in the heart of Bayelsa State, an area known for extensive oil and gas extraction activities. Environmental effects of oil and gas production may include alterations in water quality, temperature, and oxygen levels, which can affect aquatic life and fish population.49–65 Likewise, contaminants from gas flaring, such as heavy metals and polycyclic aromatic hydrocarbons, can bioaccumulate in fish, potentially posing health risks to consumers.71 The socio-economic dimensions are pivotal, as local communities rely on fisheries for both sustenance and income.

Given the gravity of these challenges, there's an urgent call for holistic policies and robust enforcement mechanisms aimed at tackling gas flaring in Nigeria and similar affected areas. These strategies must prioritize environmental preservation, safeguard public health, and advocate for sustainable energy practices. Furthermore, active engagement of local communities in decision-making processes and the promotion of alternative energy sources are imperative to reduce dependence on gas flaring. Only through unified efforts can the adverse effects of gas flaring be mitigated, paving the way for a more sustainable and just future for affected regions and communities. Thus, this study endeavors to explore the impacts of gas flaring on artisanal fisheries in the downstream region of Taylor Creek, Bayelsa State, Nigeria. The insights gained from this research will inform the formulation of sustainable environmental and fisheries management strategies in this region, which is pivotal due to its significant oil and gas activities.

Aim and objectives of the study

The aim of the study is to investigate the effects of gas flaring on artisanal fisheries in the down-stream area of Taylor Creek, Bayelsa State, Nigeria. The specific objectives of the study are to:

  1. Examine the bio-data of artisanal fishers in the down-stream area of Taylor Creek, Bayelsa State.
  2. Determine the effects on fish catch in the study area.
  3. Find out the negative effects of gas flaring on the social, economic and health of artisanal fishers in the study area.
  4. Determine other challenges occasioned by gas flaring in the study area.
  5. Provide possible measures to tackle the challenges encountered by artisanal fishers in the study area.

Methodology

Study area

The study was conducted in the down-stream area of Taylor Creek in Yenagoa Local Government Area of Bayelsa State, Nigeria from August, 2023 to January, 2024. The stretch of the down-stream area of Taylor Creek goes beyond Polaku and Okolobiri communities in Gbarain Kingdom. The down-stream area of Taylor Creek is situated between 5º 01ˈN; 6º 17ˈE and 5º 02ˈN; 6º 18ˈE (Figure 1). Several creeks and floods channels interconnect freshwater swamp forests, linking the Nun River and Taylor Creek at various points and form a mass of water body during the high flood. Okoso Creek is at present the most prominent creek connected to the Taylor Creek which subsequently empties into the Nun River at its confluence at Polaku town. In the dry and low water period, the Taylor Creek in the Zarama axis reduces to disjointed series of pools linked by sections of shallow water. The down-stream area of Taylor Creek is subject to mild tidal influence in the dry season (Kwen et al., 2019).

Figure 1 Map of Nigeria showing the Study Area.

Research design

For the study, an approach rooted in descriptive survey research design was meticulously chosen and implemented. This methodological framework offers a comprehensive and systematic approach to data collection and analysis, allowing for a detailed exploration and documentation of the phenomena under investigation. Through this design, researchers are equipped to gather pertinent information on various aspects of the subject matter, including characteristics, trends, and patterns. By employing such a design, the study aims to provide a rich and nuanced understanding of the targeted phenomenon, enabling insightful interpretation and informed decision-making.

Sampling methods

A total of 120 structured questionnaires were administered to artisanal fishers operating within the study area, specifically drawn from the Polaku, Ogboloma, Koroama, and Obunagha communities situated along the downstream stretch of Taylor Creek. Each of these communities received thirty questionnaires, strategically selected due to their proximity to the gas flaring sites or area compared to other communities along the creek's downstream section as well as their socio-economic reliance on artisanal fisheries, making them particularly vulnerable to the potential impacts of gas flaring. After a two-week period, the questionnaires were collected for analysis. The questionnaire comprised two sections: Section A focused on respondents' demographic information, encompassing details such as gender, age, marital status, religion, educational background, household size, years of fishing experience, and weekly income generation. On the other hand, Section B delved into various aspects relevant to the research topic, segmented into subsections from A to E. Utilizing a four-point rating scale, respondents were prompted to indicate their agreement with each statement, with numerical values assigned as follows: Strongly Agree (4) with a range of 3.50 to 4.49, Agree (3) with a range of 2.50 to 3.49, Disagree (2) with a range of 1.50 to 2.49, and Strongly Disagree (1) with a range of 0.50 to 1.49. Items with a mean value of 2.50 or higher were considered as agree, while those with mean values lower than 2.50 were deemed disagree, guiding the analysis process.

Limitations of the study

This study has some limitations that should be acknowledged to provide transparency and context for interpreting the findings.

  1. Reliance on self-reported data: The research heavily depended on structured questionnaires, which are subject to biases such as underreporting or overreporting due to social desirability or recall errors.
  2. Seasonal variations: The study was conducted between August 2023 and January 2024, which may not fully account for the seasonal variations in artisanal fishing activities, such as fish migration patterns, spawning activities, and fishing schedules. These dynamics could influence the findings related to fish catch and other impacts.
  3. Geographical scope: The research is geographically limited to the downstream area of Taylor Creek, Bayelsa State. While this region is significant, the findings may not be directly generalizable to other areas affected by gas flaring in the Niger Delta or beyond.
  4. Complexity of gas flaring impacts: The study primarily focused on artisanal fisheries and associated socio-economic impacts, but broader ecological and long-term health effects of gas flaring on the ecosystem and communities were not exhaustively explored.

Data analysis

The collected data underwent analysis employing straightforward descriptive statistical techniques, including percentage calculations, frequency distributions, and determination of mean scores. These analytical methods were instrumental in uncovering patterns, trends, and central tendencies within the dataset, offering a comprehensive understanding of the research findings. Through the utilization of these statistical tools, the researchers were able to distill the gathered information into meaningful insights, facilitating the interpretation and presentation of the research outcomes in a clear and concise manner.

Results

Bio-data of respondents

The bio-data of artisanal fishers (respondents) in the down-stream area of Taylor Creek is presented in Table 1. It is apparent from the results that majority of the respondents were males (65.83%) while 34.17% were females. Out of which majority (37.50%) fall into the age bracket of 30-39years, 30.87% 40-49years, 17.50% 18-29years, while only 14.17% was above 50 years. Majority of them were married (56.67%), 33.34% single, 3.33% divorced while 5.00% were widow. Majority (60.00%) were Christians, 31.67% Islam while 8.33% were other religions. Majority (40.00%) of them had secondary education, 30.00% primary education, 16.67% no-formal education while 13.33% of them had tertiary education.

Parameter

Frequency

Percentage (%)

Sex

   

Male

79

65.83

Female

41

34.17

Total

120

100

Age

   

18-29

21

17.5

30-39

45

37.5

40-49

37

30.87

50 and above

17

14.17

Total

120

100

Marital Status

 

Single

42

35

Married

68

56.67

Divorce

4

3.33

Widow

6

5

Total

120

100

Religion

   

Christianity

72

60

Islamic

38

31.67

Others

10

8.33

Total

120

100

Educational Level

 

No-Formal Education

20

16.67

Primary Education

36

30

Secondary Education

48

40

Tertiary Education

16

13.33

Total

120

100

Table 1 Bio-data (Personal Data) of artisanal fishers in the down-stream area of Taylor Creek

Source: Field Survey, 2023-2024

The Household size of respondents

The results of house hold size is represented in Figure 2 and it shows that majority (45.00%) of the respondents had a household size 6-10 persons, followed by 1-5 persons (38.33%) and only 16.67% of them had over 11 persons.

Figure 2 Household size of artisanal fishers in the down-stream area of Taylor Creek.

Years of fishing experience of artisanal fishers

Results shows that majority (42.50%) of the artisanal fishers in the study area had 11-15 years fishing experience, followed by 6-10 years (30.83%), over 16 years (18.33%) and 8.33% alone had 1-5 years of fishing experience (Table 2 and Figure 3).

Figure 3 Distribution of Years of Experience.

Year of experience

Frequency

Percentage (%)

1-5 Yrs.

10

8.33

6-10 Yrs.

37

30.83

11-15 Yrs.

51

42.5

Over 16 Yrs.

22

18.33

Total

120

100

Table 2 Years of fishing experience of artisanal fisher in the down-stream area of Taylor Creek

Source: Field Survey, 2023-2024.

Weekly income generated by artisanal fishers

The weekly income generated by artisanal fishers in the study area is shown in Figure 4. Majority (45.83%) of the fishers generated up to #21,000 to #30,000 weekly, followed by #31,000 to #40,000 (35.00%), #10,000 to #20,000 (15.00%) and only 4.17% generated #41,000 to #50,000.

Figure 4 Weekly income generated by artisanal fishers in the down-stream area of Taylor Creek.

Effects of gas flaring on fish catch

Table 3 and Figure 5 describes the effects of gas flaring on fish catch in the study area. Out of the artisanal fishers interviewed, majority (46.18%) said gas flaring has resulted to low fish catch in the study area and 1.42% disagree with that view. Few (4.02%) persons said it has led to high fish catch and majority (31.34%) disagreed with that fact, 1.61% said gas flaring has made them to have moderate fish catch and 33.05% disagree with that opinion. All the respondents said that gas flaring has not led to no fish catch (34.19%) in the area for now. In the same vein, all the fishers interviewed unanimously said that gas flaring has resulted to high cost of fish prices in the study area.

Effect

Yes

Percentage (%)

No

Percentage (%)

Low fish catch

115

46.18

5

1.42

High fish catch

10

4.02

110

31.34

Moderate fish catch

4

1.61

116

33.05

No fish catch

0

0

120

34.19

High cost of fish

120

48.19

0

0

Total Number

249

 

351

 

Table 3 Effects of gas flaring on fish catch in the down-stream area of Taylor Creek

Source: Field Survey, 2023-2024.

Figure 5 Effects on Fish Catch and Costs.

Negative effects of gas flaring on social, economic and health of artisanal fishers

Table 4 and Figure 6 below illustrates the multifaceted adverse impacts of gas flaring on the social, economic, and health aspects affecting artisanal fishers in the downstream vicinity of Taylor Creek. The findings reveal a consensus among respondents, with 7.71% unanimously acknowledging the significant reduction in fish catch resulting from gas flaring activities. Additionally, 7.26% of respondents concur that gas flaring indiscriminately leads to fish mortality within the creek, while 5.83% express disagreement with this notion. Notably, 6.87% of artisanal fishers agree that the altered dynamics of the water body due to gas flaring disrupt their fishing schedules, with 10.83% holding a contrary perspective. Furthermore, 6.68% of respondents acknowledge the detrimental effects of gas flaring on the reproductive functions and spawning activities of fish, while 5.00% express disagreement. Migration of fish fauna is also perceived as a consequence of gas flaring, with 6.29% in agreement and 23.33% opposed to this notion. Economically, all respondents (7.71%) unanimously affirm that gas flaring significantly impacts their daily, weekly, monthly, and annual income. Similarly, 7.46% acknowledge the role of gas flaring in causing diseases among both humans and fish, while 3.33% hold a differing perspective. Furthermore, all respondents (7.71%) agree that gas flaring disrupts the primary source of livelihood for fishers, and 7.58% express concerns about the potential extinction of certain fish species due to gas flaring, although 16.67% disagree with this assertion. Socially and economically, respondents unanimously (7.71%) agree that gas flaring imposes hardships on both fishers and the local populace. Moreover, 6.68% of respondents acknowledge the involvement of the ruling class in corrupt practices linked to oil and gas companies, while 13.33% refute this claim. Additionally, 6.04% agree that gas flaring poses risks of human and financial resource losses, with 21.67% holding a differing viewpoint. Concerns about the adverse impact of gas flaring on fishing activities are shared by all respondents (7.71%), while only 0.88% acknowledge its role in ecosystem destruction, and 15.00% contest this assertion.

Effect

Agree

Percentage (%)

Disagree

Percentage (%)

Drastic reduction of fish catch

120

7.71

0

0

Causes death of fish in the creek indiscriminately

113

7.26

7

5.83

Fishers don’t know the right time to go out for fishing again because it has changed the dynamics of the water body

107

6.87

13

10.83

Destruction of spawning activities and reproductive functions of the fish

104

6.68

6

5

Causes migration of fish fauna

98

6.29

28

23.33

Fishers daily, weekly, monthly and annual income is affected

120

7.71

0

0

Causes diseases to man and the fish

116

7.46

4

3.33

Fishers source of livelihood is affected

120

7.71

0

0

Causes the extinction (disappearance) of some fish species

118

7.58

2

1.67

Causes social and economic hardship to the fishers and the people in the area

120

7.71

0

0

Corruption of the ruling class in amassing wealth through collaborations with oil and gas companies

104

6.68

16

13.33

The fishers and people stands to lose both human and financially resources

94

6.04

26

21.67

Fishing is affected in the area

120

7.71

0

0

Causes destruction of the ecosystem

102

0.88

18

15

Total Number

1,556

 

120

 

Table 4 Negative effects of gas flaring on the social, economic and health of artisanal fishers

Source: Field Survey, 2023-2024

Figure 6 Impact Assessment Based on Agreement and Disagreement.

Other challenges occasioned by gas flaring on artisanal fisheries

Table 5 and Figure 7 below sheds light on additional challenges stemming from gas flaring impacting artisanal fisheries operating in the downstream region of Taylor Creek, Bayelsa State. The results unveil a spectrum of mean values ranging between 3.37 (the lowest) and 4.21 (the highest), derived from respondents' assessments. Notably, the mean scores signify varying degrees of severity attributed to each identified challenge. Among these challenges, the fluctuation of water temperature beyond normal stands at 3.45, indicating a significant concern for fishers. Moreover, the issue of low income rates garners a mean score of 3.85, highlighting the economic repercussions faced by artisanal fishers. Similarly, the destruction of fish size classes receives a mean score of 3.61, reflecting the detrimental impact on fish populations. Additionally, the phenomenon of many artisanal fishers abandoning the fishing sector registers a mean score of 3.93, suggesting the severity of this trend. Moreover, the necessity for artisanal fishers to spend extended hours hunting for fish is underscored by a mean score of 4.21, emphasizing the increased labor intensity imposed by gas flaring. Furthermore, the rapid degradation of fishing implements leading to spoilage is denoted by a mean score of 3.37, signifying material losses incurred by fishers. The destruction of aquatic micro and macro fauna and flora is highlighted by a mean score of 3.87, illustrating the ecological consequences of gas flaring. Finally, the introduction of trace and heavy metals into the creek receives a mean score of 3.43, pointing to environmental contamination concerns. These findings collectively underscore the multifaceted challenges faced by artisanal fisheries in the downstream area of Taylor Creek due to the impacts of gas flaring, necessitating comprehensive mitigation strategies to safeguard both the ecological and socio-economic well-being of the affected communities.

S/N

Item

SA

A

D

SD

TN

_ X

Remark

1

Fluctuation of water temperature beyond normal

67

43

7

3

120

3.45

Agree

   

268

129

14

3

414

   

2

Low income rate

102

18

0

0

120

3.85

Strongly Agree

   

408

54

0

0

462

   

3

Destruction of size class of fish

83

31

2

4

120

3.61

Strongly Agree

   

332

93

4

4

433

   

4

Making many artisanal fishers abandoning the fishing sector

113

6

1

0

120

3.93

 Strongly Agree

   

452

18

2

0

472

   

5

Making artisanal fishers spending more hours in hunting for fish

115

15

0

0

120

4.21

 Strongly Agree

   

460

45

0

0

505

   

6

Fishing implements undergo quick degradation and leading to spoilage

53

62

2

3

120

3.37

Agree

   

212

186

4

3

405

   

7

Destruction of aquatic micro and macro fauna and flora

105

14

1

0

120

3.87

Strongly Agree

   

420

42

2

0

464

   

8

Introduction of trace and heavy metals into the creek

66

44

6

4

120

3,43

Agree

   

264

132

12

4

412

   

Table 5 Mean responses of artisanal fishers on other challenges occasioned by gas flaring in artisanal fisheries in the down-stream area of Taylor Creek

Criterion Mean = 2.50

Key: SA, strongly agree, A, agree, SD, strongly disagree, D, disagree, TN, total number

Figure 7 Impact Assessment Based on Average Score.

Possible measures to tackle the challenges encountered by artisanal fishers

Table 6 and Figure 8 below presents the collective response of artisanal fishers regarding potential measures aimed at addressing the challenges encountered within the downstream area of Taylor Creek. The findings elucidate a range of mean scores spanning from 3.70 (the lowest) to 4.00 (the highest), derived from the respondents' perspectives. These mean scores provide insights into the perceived efficacy and importance of each proposed measure in mitigating the identified challenges. Among the proposed measures, utilizing gas for either gas injection or gas lift emerges with a mean score of 3.70, highlighting its potential profitability and economic viability compared to gas flaring. Similarly, leveraging gas for electricity generation through cogeneration, gas turbines, and steam turbines garners the highest mean score of 4.00, underscoring its perceived effectiveness in addressing energy needs while minimizing environmental impact. Additionally, liquefying gas for storage in vessels or bottles as liquid natural gas receives a mean score of 3.95, indicating its feasibility as an alternative approach.

S/N

Item

SA

A

D

SD

TN

_

X

Remark

1

Gas should be used for either gas injection or gas lift which is more profitable and economical compared to gas flaring

81

39

0

0

120

3.7

Strongly Agree

   

324

117

0

0

441

   

2

Gas should be used for electricity generation through the use of cogeneration, gas turbines and steam turbines

120

0

0

0

120

4

Strongly Agree

   

480

0

0

0

480

   

3

To liquefy the gas and stored in vessels or bottles as liquid natural gas

114

6

0

0

120

3.95

Strongly Agree

   

456

18

0

0

474

   

4

By compressing natural gas to less than 1% of the volume it occupies at standard atmospheric pressure

111

9

0

0

120

3.93

 Strongly Agree

   

444

27

0

0

471

   

5

Government should make provision for the restoration of the extraction areas

120

0

0

0

120

4

 Strongly Agree

   

480

0

0

0

480

   

6

Companies should carry out safe and environmentally friendly operation in order to prevent degradation of the environment

118

2

0

0

120

3.98

Strongly Agree

   

472

6

0

0

478

   

7

New laws should be made in order to preserve the environment and also get more qualified personnel to ensure that the laws are adhered to by the companies

105

15

0

0

120

3.88

Strongly Agree

   

420

45

0

0

465

   

Table 6 Mean responses of artisanal fishers on possible measures to tackle the challenges encountered by artisanal fishers in the study area

Criterion Mean = 2.50

Key: SA, strongly agree, A, agree, SD, strongly disagree, D, disagree, TN, total number

Figure 8 Preferred Gas Utilization Strategies Based on Average Scores.

Furthermore, compressing natural gas to reduce its volume to less than 1% of its standard atmospheric pressure registers a mean score of 3.93, suggesting its potential in facilitating efficient gas management practices. Government provision for the restoration of extraction areas garners a mean score of 4.00, emphasizing the importance of environmental remediation efforts. Similarly, ensuring companies carry out safe and environmentally friendly operations to prevent environmental degradation receives a mean score of 3.98, underscoring the necessity for responsible industrial practices. Lastly, the implementation of new legislation aimed at environmental preservation, coupled with the recruitment of qualified personnel for enforcement, is highlighted with a mean score of 3.88, signaling the importance of regulatory frameworks and competent oversight in safeguarding the environment and promoting sustainable practices. These findings collectively underscore the significance of adopting multifaceted approaches encompassing technological, regulatory, and environmental restoration strategies to address the challenges faced by artisanal fishers in the downstream area of Taylor Creek.

Discussion

Bio-data of artisanal fishers

The demographic profile of artisanal fishers observed in this study aligns closely with findings reported by several previous studies, including those conducted by Davies and Kwen,72 Kwen and Nwabeze,73 Ayanboye and Adedokun (2015), and Aghoghovwia et al.74 Consistent with these reports, artisanal fisheries emerge as a domain engaged by individuals of both genders, with a noticeable prevalence of males, particularly within the economically active age bracket of 30 to 39 years. These studies collectively underscore the predominant participation of men in fishing activities, a trend that resonates with the observations made in the present study. Notably, the work of Kwen and Nwabeze73 accentuates the significant role played by women in the artisanal fisheries sector, emphasizing their active involvement in fish processing, marketing, and various social aspects related to fisheries within Nigerian fishing communities (Odubo and Anele, 2019; Raimi and Odubo, 2022).75–78 This acknowledgment of women's contributions underscores the multifaceted nature of artisanal fishing activities, wherein both men and women play integral roles across different facets of the industry. Thus, recognizing these contributions is critical for shaping policies that ensure equitable access to resources, gender-sensitive interventions, and targeted skill development programs for women.

For example, community-level training initiatives for women fish processors and marketers could enhance their income-generating potential while promoting inclusive development in artisanal fisheries. Such insights underscore the importance of recognizing and valuing the diverse contributions of both genders within the artisanal fisheries sector, thereby fostering a more inclusive and equitable approach to fisheries management and development initiatives. The prevalence of male fishers dominating the downstream region of Taylor Creek can be attributed to the influence of gender disparities in occupational choices, particularly within the fishing and fish farming sectors in this locale. This gender disparity arises due to the demanding nature of active fishing operations compared to passive fishing endeavors, where the labor intensity involved tends to favor male participation. These findings echo the observations of Tagago et al.79 Davies and Kwen,72 and Ayanboye and Adedokun (2015), who similarly noted that fishing activities predominantly attract individuals within the age range of 30 to 40 years. This age distribution may stem from the inherent attributes of younger individuals, who exhibit higher levels of enthusiasm for exploring new practices in fisheries and fishing operations. Additionally, their mental acuity and receptiveness to innovative ideas in fishing gear development techniques contribute to their active engagement in the industry.

The significant representation of married fishers observed in the study area mirrors the findings of Kwen et al.73 and Aghoghovwia et al.,74 who documented a similar trend in the artisanal fisheries sector. This phenomenon could be attributed to the greater responsibilities and obligations typically borne by married individuals, as they navigate familial duties and financial commitments. Furthermore, the prevalence of artisanal fishers with primary and secondary education aligns with the observations of Adeparusi et al. (2003). This relatively high level of literacy among fishers in the study area empowers households with the capacity to implement effective income diversification strategies, thereby mitigating income fluctuations, averting income failures, and alleviating poverty within these communities. Such insights underscore the complex interplay of socio-economic factors shaping the occupational landscape of artisanal fisheries and highlight the importance of addressing gender disparities and promoting educational opportunities to foster inclusive and sustainable livelihoods within these communities.

Effects of gas flaring on artisanal fisheries

The findings of this study corroborate with the research findings of Omohimoria et al.80 and Udok and Akpan (2017), both of whom underscored the detrimental impact of gas flaring on the aquatic environment. Such adverse effects encompass the destruction of freshwater ecological systems, depletion of aquatic fauna, as well as socio-economic hardships and the loss of vital fishing grounds. Further validating these observations, an impact assessment conducted by Powell and White (1985) following the 1983 Oshika gas flare incident in Rivers State confirmed severe consequences, including the demise of floating and submerged aquatic vegetation such as water lettuce, along with mortality among fin and shellfish, mangrove forest devastation, and detrimental effects on aquatic bird populations. Additionally, the development initiatives within the region have contributed to site degradation, diminishing their ecological value and utility. Supporting evidence from Ubani and Onyejekwe81 and Uwem and Enobong (2017) further underscores the multifaceted nature of gas flaring's impacts, with emphasis placed on environmental, health, and various other implications. These scholars highlight the far-reaching consequences of gas flaring beyond ecological degradation, encompassing adverse effects on human health and socio-economic well-being.

Such comprehensive assessments underscore the urgent need for holistic approaches to address the challenges posed by gas flaring, encompassing environmental protection, public health interventions, and sustainable development strategies. These collective insights underscore the imperative for concerted action to mitigate the adverse effects of gas flaring and promote the sustainable management of natural resources in affected regions. Over the past five decades, the persistent practice of gas flaring and venting associated with petroleum exploration and production activities in the Niger Delta region of Nigeria has perpetuated a multitude of complex consequences across various dimensions including energy, natural environment, socio-economic landscape, human health, and sustainable development. The prevalence of flaring gas has inflicted significant suffering and destruction upon human populations, flora, and fauna alike. Studies conducted by Kindzierski et al.82 and Ozogu-Agbe et al.83 have illuminated the detrimental effects of gas flaring in the Niger Delta, specifically noting adverse changes in the hematological attributes of aquatic organisms. These alterations, including negative impacts on blood and blood-forming cells, have been implicated in conditions such as aplastic anemia, pancytopenia, and leukemia. To address these challenges, lessons can be drawn from successful mitigation measures implemented in similar regions. For instance, in Ecuador, community-led reforestation projects have helped restore damaged aquatic ecosystems, while in Norway, strict environmental regulations and gas reinjection technologies have drastically reduced flaring activities.

Policymakers in Nigeria could adopt and adapt these strategies, ensuring context-specific solutions that balance ecological preservation with economic development. Beyond the immediate health and environmental ramifications, the nation also faces substantial economic losses, with billions of dollars' worth of gas wasted through routine flaring, literally incinerated into the atmosphere on a daily basis. This squandered resource could be harnessed for domestic consumption and electricity generation, potentially alleviating the nation's chronic energy deficits (Raimi et al., 2024).14,67 Efforts directed towards gas utilization for power generation have the potential to significantly bolster electricity production,50,84 thereby bridging the gap between supply and national demand. As underscored by Effiong and Etowa,85 Nigeria has incurred considerable revenue losses as a direct consequence of gas flaring and oil spillages, further exacerbating economic challenges and hindering national development efforts.

These revelations underscore the urgent imperative for comprehensive measures aimed at curbing gas flaring, optimizing resource utilization, and mitigating the far-reaching impacts on human health, environmental integrity, and economic sustainability within the Niger Delta region and beyond. The investigation conducted in the study area unveiled the profound economic hardships inflicted upon its inhabitants by the practice of gas flaring. This observation resonates strongly with the findings documented by Arowolo and Adaja,86 who similarly highlighted the adverse economic consequences associated with gas flaring in affected regions. Moreover, the research conducted by Osuagwu and Olaifa87 underscored the detrimental impact of environmental contamination resulting from gas flaring on fishing activities, manifesting in various detrimental outcomes such as fish mortality, depletion of fish stocks, reduced catch rates, and even prompting some fishers to discontinue their fishing endeavors altogether. Bayode et al.88 further corroborated these assertions, emphasizing the deleterious effects of gas flaring on aquatic ecosystems, including the pollution of water bodies,40–50,89,90 destruction of fish habitats,91,92 and the degradation of mangrove forests (Olalekan et al., 2021; Raimi et al., 2022d, e).49,93,94

Additionally, Bayode et al.88 highlighted the consequential decline in fish production and the abandonment of fishing grounds in Ondo State, further exacerbating the challenges faced by artisanal fishers and compromising their livelihoods. The repercussions of diminished fish production extend beyond economic concerns, posing a significant threat to the sustainability of fishing activities and the well-being of communities reliant on them. As articulated by Chijioke et al.,95 the contamination of aquatic environments compels artisanal fishers in affected communities to forsake their traditional livelihoods, abandoning their fishing equipment, canoes, and even farmlands in search of alternative sources of income. This cascade of adverse effects underscores the urgent need for comprehensive interventions aimed at mitigating the impacts of gas flaring on both the economic viability and environmental integrity of affected regions. Such initiatives should prioritize the restoration of aquatic ecosystems, support for alternative livelihoods, and sustainable resource management practices to safeguard the welfare of communities’ dependent on artisanal fisheries. In addition to gas flaring, Osuagwu and Olaifa87 elucidated a myriad of other environmental factors that significantly impede fishing activities within aquatic environments. These factors encompass incidents such as oil well blowouts, pipeline seepages, and the inadequate disposal of drilling fluids.

Furthermore, Ana et al.96 conducted a comprehensive study in the Eleme and Ahoada East areas of Rivers State, Nigeria, aimed at evaluating the prevalence of health consequences associated with exposure to various environmental risk factors stemming from oil pollution and gas flare incidents. Their findings underscored a stark discrepancy in morbidity rates between the two communities, with Eleme exhibiting notably higher incidences compared to Ahoada East. The documented morbidity cases encompassed a spectrum of health ailments, including skin diseases, respiratory disorders, and cancer. These revelations serve to underscore the profound health and environmental ramifications stemming from not only gas flaring but also the broader spectrum of environmental hazards prevalent within oil-producing regions. Such insights underscore the imperative for robust regulatory measures, effective environmental management strategies, and comprehensive health interventions to mitigate the adverse impacts on both human health and ecological integrity within affected communities.

Possible measures to tackle the challenges encountered by artisanal fishers

The potential measures identified to address the challenges confronted by artisanal fishers, as documented in this study, closely align with the recommendations put forth by Ozogu-Agbe et al.83 and Ajayi et al.67 These proposals advocate for governmental intervention aimed at intensifying strategic efforts to convert flared gases into viable resources, such as cooking/domestic gas and electricity generation. Similarly, the suggestions echo the sentiments expressed by Ibrahim et al. (2009), emphasizing the utilization of gas for purposes such as gas injection or gas lift, known for their profitability and economic viability compared to conventional gas flaring practices. Additionally, the utilization of gas for electricity generation through cogeneration, gas turbines, and steam turbines emerges as a pragmatic solution, in line with the imperative to maximize energy efficiency and minimize environmental impact. Moreover, the proposals underscore the importance of liquefying gas for storage as liquid natural gas, as well as compressing natural gas to facilitate efficient utilization. Furthermore, the imperative for governmental provision for the restoration of extraction areas and the implementation of stringent regulations to ensure safe and environmentally friendly operations by companies are emphasized.

Additionally, successful initiatives such as the Global Gas Flaring Reduction Partnership (GGFRP) by the World Bank highlight the potential for collaborative approaches. These efforts can serve as a blueprint for Nigeria, emphasizing community involvement, awareness campaigns, and resource-sharing frameworks to mitigate the impacts of gas flaring on artisanal fishers. For instance, empowering fishers through alternative livelihoods, like aquaculture or eco-tourism, could help diversify income sources while reducing dependency on environmentally degraded fishing grounds. These measures not only aim to mitigate environmental degradation but also seek to uphold ecological integrity and safeguard the well-being of local communities. Moreover, the global initiative spearheaded by the World Bank, in collaboration with countries, oil companies, and development institutions through the Global Gas Flaring Reduction Partnership, underscores the collective efforts towards mitigating the impact of gas flaring on a global scale. This collaborative endeavor aims to explore avenues for conserving gas resources, creating markets for its sale, or promoting its utilization in environmentally friendly applications. Such concerted efforts signify a paradigm shift towards sustainable resource management practices and underscore the imperative for global cooperation in addressing the challenges posed by gas flaring.97–119

Conclusion

The environmental ramifications of gas flaring in the downstream area of Taylor Creek are profound and far-reaching. This study unequivocally demonstrates that gas flaring has precipitated a myriad of environmental crises, including the pollution of creek water, widespread ecosystem degradation, and mass mortality among fish and other aquatic organisms. The observed deterioration of the ecosystem underscores a concerning trend exacerbated by the lax enforcement of existing environmental protection laws and regulations. The failure of governmental bodies to ensure stringent compliance with these regulations has further compounded the pollution of the downstream area of Taylor Creek, perpetuating ecological imbalances and undermining the region's environmental integrity. Conclusively, the study advocates for a multifaceted approach to mitigate the environmental pollution resulting from gas flaring activities in the study area. It is recommended that the gas currently being flared be utilized more efficiently and sustainably. Specifically, gas injection or gas lift techniques should be prioritized due to their enhanced profitability and economic viability compared to traditional flaring practices. Furthermore, gas should be harnessed for electricity generation through cogeneration, employing gas turbines and steam turbines to maximize energy output

Additionally, efforts should be directed towards liquefying gas and storing it in vessels or bottles as liquid natural gas, as well as compressing natural gas to occupy less than 1% of its volume at standard atmospheric pressure. These methods offer efficient means of storage and transportation, minimizing waste and environmental impact. Moreover, governmental intervention is imperative to facilitate the restoration of extraction areas affected by gas flaring activities. Strict enforcement of environmental regulations is essential to compel companies to undertake safe and environmentally friendly operations, thereby preventing further degradation of the environment. Finally, the enactment of new legislation aimed at preserving the environment and bolstering regulatory oversight is crucial. Strengthening the enforcement capacity through the recruitment of qualified personnel is essential to ensure compliance with environmental laws by companies operating in the region. By implementing these comprehensive measures, significant strides can be made in curbing the environmental pollution associated with gas flaring activities in the study area, fostering a more sustainable and ecologically resilient environment for present and future generations.

Recommendations

Based on the research findings, the following recommendations are put forth:

  1. Implementation of Modernized Technologies: Oil companies should adopt advanced technologies aimed at minimizing the release of pollutants into the environment, thereby reducing environmental degradation. Local governments and community organizations can play a pivotal role by advocating for and monitoring the adoption of such technologies in their areas, ensuring accountability and compliance.
  2. Enforcement of Environmental Laws: The government should rigorously enforce existing environmental laws and regulations. Additionally, there should be a review and adjustment of these regulations to incorporate innovative methods and practices employed in environmentally conscious countries such as Saudi Arabia, Russia (Siberia), United States (Texas), Venezuela (Orinoco Belt), Canada and Norway. Local governments could work closely with federal authorities to ensure these laws are applied effectively at the community level, providing support for inspection teams and facilitating local reporting mechanisms for non-compliance.
  3. Enhancement of Corporate Social Responsibility (CSR) or Creating Shared Value (CSV): Oil companies should enhance their Corporate Social Responsibility initiatives to better address the socioeconomic needs of the local communities affected by their operations. Community organizations can act as intermediaries, identifying the most pressing local needs, such as education, healthcare, or alternative livelihoods, and engaging oil companies to prioritize these areas in their CSR programs.
  4. Establishment of Independent Environmental Regulatory Body: There is a need for the establishment of an independent regulatory body specifically dedicated to overseeing environmental matters within the oil and gas industry. This body should operate autonomously from entities like the Department of Petroleum Resources and the Nigerian National Petroleum Corporation. Local governments can collaborate with this regulatory body by providing on-ground support for environmental audits, assisting in data collection, and facilitating community consultations.
  5. Implementation of Greenhouse Emission Regulations: Stringent regulations should be instituted to monitor and regulate the greenhouse gas emissions resulting from gas flaring activities conducted by oil companies. Local governments can introduce community-level emission monitoring programs, involving trained local volunteers or organizations to regularly report on flaring activities and ensure compliance with these regulations.
  6. Public Awareness Campaigns: Public enlightenment campaigns should be conducted to educate individuals about the adverse impacts of operations such as gas flaring on human health and the environment. Many individuals may not fully comprehend the risks associated with these activities. Local governments and community organizations can lead these campaigns, utilizing town hall meetings, local radio stations, and schools to disseminate information effectively to all community members.
  7. Inclusion of Gas Storage Facilities in Contracts: The government should mandate the inclusion of provisions for the construction of gas storage facilities in contracts with International Oil Companies (IOCs) and other oil-producing entities. This initiative can help address the electricity shortage in the country by utilizing gas for power generation. Community organizations could engage with policymakers and advocate for the inclusion of such provisions, emphasizing the direct benefits for local communities, such as improved access to energy and reduced environmental harm.
  8. By implementing these recommendations and leveraging the active participation of local governments and community organizations, stakeholders can collectively work towards mitigating the environmental and socioeconomic challenges associated with oil and gas operations. Such collaborative efforts will foster a more sustainable and equitable future for all.

Future research directions

The following areas of research should be explored to deepen understanding and provide actionable insights:

  1. Long-term and cumulative impacts: Future research should focus on longitudinal studies to assess the cumulative ecological and socio-economic effects of gas flaring over extended periods. This includes impacts on biodiversity, water quality, and public health.
  2. Alternative livelihood strategies: Investigating the feasibility of alternative livelihoods, such as aquaculture, eco-tourism, or renewable energy ventures, could help communities reduce their reliance on artisanal fishing in regions heavily impacted by gas flaring.
  3. Comparative regional studies: Conducting comparative studies across multiple regions within the Niger Delta or globally could identify variations in the effects of gas flaring and uncover best practices for mitigation and adaptation.
  4. Role of seasonal variations: Research examining how seasonal changes affect fish catch, species migration, and spawning in gas-flaring regions will provide critical insights into managing fisheries more sustainably.
  5. Policy impact assessments: Assess the effectiveness of implemented policies and regulations in curbing gas flaring and their impact on local livelihoods. This could guide more effective policymaking.
  6. Community-driven solutions: Studies focusing on the role of local governments and community organizations in addressing the challenges posed by gas flaring could provide practical solutions. This includes examining participatory decision-making and grassroots advocacy.

By addressing these areas, future research can contribute to developing sustainable environmental, economic, and social strategies for communities affected by gas flaring.

Significance statement

The study “Making the Invisible Visible: The Effects of Gas Flaring on Artisanal Fisheries in the Down-Stream Area of Taylor Creek, Bayelsa State, Nigeria” sheds light on the significant impact of gas flaring on artisanal fisheries, a crucial economic activity in the region. Through structured questionnaires and descriptive survey research, the study reveals profound effects, including drastic reductions in fish catch, extinction of certain species, increased fish prices, indiscriminate fish mortality, disrupted fishing schedules, altered water dynamics, impaired spawning activities, and economic hardships for fishers. Furthermore, gas flaring contributes to fish size reduction, abandonment of fishing, increased time spent on fishing, and accelerated degradation of fishing implements. Urgent measures are required to mitigate these adverse effects, including utilizing gas flaring for beneficial purposes, government intervention to restore extraction areas, adoption of safe operational practices by companies, and enactment of legislation to protect the environment and control pollution. These recommendations are vital for preserving the local ecosystem and sustaining artisanal fisheries in the region. Thus, graphically it is represented (Figure 9) as:

Figure 9 Steps to Mitigate Gas Flaring Impact.

Preprint version

Kwen Keme-Iderikumo, Eli Akayinaboderi Augustus, Morufu Olalekan Raimi. (2024). Making the Invisible Visible: The Effects of Gas Flaring on Artisanal Fisheries in the Down-Stream Area of Taylor Creek, Bayelsa State, Nigeria. Qeios. doi:10.32388/UIM59Z.

Acknowledgments

This manuscript did not receive any specific grant from any funding agencies. Authors are thankful to Federal University Otuoke for providing all necessary administrative supports.

Conflicts of interest

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

References

  1. Edino MO, Nsofor GO, Bombom LS. Perceptions and Attitudes towards Gas Flaring in the Niger Delta, Nigeria. Energy. 2010;30:67–75.
  2. World Bank. Regulation of Associated Gas Flaring and Venting: A Global Overview and Lessons from International Experience (English). Global Gas Flaring Reduction - A Public-Private Partnership. No. 3. Washington, DC: World Bank. 2011.
  3. Premoboere EA, Raimi MO. Corporate Civil Liability and Compensation Regime for Environmental Pollution in the Niger Delta. International Journal of Recent Advances in Multidisciplinary Research. 2018;05(06):3870–3893.
  4. Raimi MO, Omidiji AO, Adio ZO. Health Impact Assessment: A Tool to Advance the Knowledge of Policy Makers Understand Sustainable Development Goals. Conference paper presented at the: Association for Environmental Impact Assessment of Nigeria (AEIAN) On Impact Assessment: A Tool for Achieving the Sustainable Development Goals in Nigeria, 7th and 8th November, 2019 in University of Port Harcourt. 2019.
  5. Raimi MO, Tonye VO, Omidiji AO. Environmental Health and Climate Change in Nigeria. World Congress on Global Warming. Valencia, Spain. 2018.
  6. Obi N, Akuirene A, Bwititi P. Impact of Gas Flaring on Communities in Delta Region of Nigeria, Narrative Review Part 1: Environmental Health Perspective. International Journal of Scientific Reports. 2021;7(3):186–193.
  7. Morufu R, Timothy KS, Ajayi BS, et al. Air of Uncertainty from pollution profiteers: Status of ambient air quality of sawmill industry in Ilorin Metropolis, Kwara State, Nigeria. Research Journal of Ecology and Environmental Sciences. 2021a.
  8. Omoyajowo K, Raimi M, Waleola T, et al. Public Awareness, Knowledge, Attitude and Perception on Microplastic Pollution around Lagos Lagoon. Ecological Safety and Balanced use of Resources. 2022;2(24):35–46.
  9. Clinton-Ezekwe IC, Osu IC, Ezekwe IC, et al. Slow death from pollution: potential health hazards from air quality in the mgbede oil fields of south-south Nigeria. Open Access J Sci. 2022;5(1):61‒69.
  10. Omoyajowo KO, Raimi MO, Omoyajowo KA. Towards a Reduced Pollution Society: Systematic Review on the Role of Storytelling, Social Media, Humor and Celebrities’Influence for Research Communication. J Appl Sci Environ Manage. 2024;28(2):603–623.
  11. World Bank. Defining an Environmental Development Strategy for the Niger Delta Volume Ii Annexes Contents. 2002;2.
  12. Ekpoh I, Obia A. The Role of Gas Flaring in the Rapid Corrosion of Zinc Roofs in the Niger Delta Region of Nigeria, The Environmentalist. 2010;30(4):347–352.
  13. Raimi MO, Sabinus CE. An Assessment of Trace Elements in Surface and Ground Water Quality in the Ebocha-Obrikom Oil and Gas Producing Area of Rivers State, Nigeria. International Journal for Scientific and Engineering Research (Ijser). 2017;8(6).
  14. Ebuete AW, Raimi MO, Ebuete IY, et al. Renewable Energy Sources for the Present and Future: An Alternative Power Supply for Nigeria. Energy and Earth Science. 2019;2(2):27.
  15. Font R, Johnson K, Smith L. Impacts of Gas Flaring in the Niger Delta Region of Nigeria. Sustainability. 2019;11(7):2156.
  16. Raimi MO, Adio ZO, Odipe OE, et al. Impact of Sawmill Industry on Ambient Air Quality: A Case Study of Ilorin Metropolis, Kwara State, Nigeria. Energy and Earth Science. 2020b;3(1).
  17. Deinkuro NS, Charles WK, Raimi MO, et al. Oil Spills in the Niger Delta Region, Nigeria: Environmental Fate of Toxic Volatile Organics. 2021a.
  18. Ifeanyichukwu CE, Christian LO, Morufu OR, et al. Hydrocarbon-Based Contaminants in Drinking Water Sources and Shellfish in the Soku Oil and Gas Fields of South-South Nigeria. Open Journal of Yangtze Gas and Oil. 2022;7.
  19. Awogbami SO, Solomon OA, Sawyerr OH, et al. Comparative Assessment of Seasonal Variations in the Quality of Surface water and its associated health hazards in Gold Mining Areas of Osun State, South-West Nigeria. PREPRINT (Version 1) available at Research Square. 2022.
  20. Clinton-Ezekwe I, Raimi MO, Ezekwe IC. Ensuring Safety: Groundwater Quality and Its Potential Health Effects in the Mgbede Oil Fields Environment of South-South Nigeria. JMIR Preprints. 2024a;64294.
  21. Clinton-Ezekwe I, Raimi M, Ezekwe I, et al. From Oil to Health: Groundwater Quality and Its Potential Health Effects in Mgbede Oil Fields of South-South Nigeria. Open Journal of Yangtze Oil and Gas. 2024b;9:95–118.
  22. Fubara GE, Dokuboba A, Ilemi JS. The Niger Delta is Under a Pollution Warning: Hydrocarbon profiles in crude oil polluted soil remediated with Pleurotus ostreatus and Eisenia fitida. bioRxiv 2024a.06.04.597352.
  23. Fubara GE, Ukoima HN, Dokuboba A. Evaluating Bioremediation Strategies on Microbial Diversity in Crude Oil-Contaminated Soil Over Three to Six Months in Port Harcourt, Nigeria., 14 May 2024, PREPRINT (Version 1) available at Research Square. 2024b.
  24. Evans FG, Nkalo UH, Amachree D, et al. From Killer to Solution: Evaluating Bioremediation Strategies on Microbial Diversity in Crude Oil-Contaminated Soil over Three to Six Months in Port Harcourt, Nigeria. Adv Environ Eng Res. 2024;5(4):023.
  25. Fubara G, Amachree D, Soberekon I, et al. From Crisis to Recovery: Addressing Hydrocarbon Pollution in Niger Delta Soils Treated with Pleurotus ostreatus and Eisenia fitida. Open Journal of Yangtze Oil and Gas. 2025;10:1–29.
  26. Manby B. The Price of Oil: Corporate Responsibility and Human Rights Violations in Nigeria's Oil Producing Communities. Human Rights Watch, New York. 1999. p. 202.
  27. Akindele EO, Adekunle IM, Asaolu SS. Impact of Gas Flaring on Fish and Fisheries in the Niger Delta, Nigeria: A Review. Open Journal of Ecology. 2016;6(08):441–450.
  28. Omidiji AO, Raimi MO. Practitioners Perspective of Environmental, Social and Health Impact Assessment (ESHIA) Practice in Nigeria: A Vital Instrument for Sustainable Development. Paper Presented at the Association for Environmental Impact Assessment of Nigeria (AEIAN) On Impact Assessment: A Tool for Achieving the Sustainable Development Goals in Nigeria, 7th and 8th November, 2019.
  29. Suleiman RM, Raimi MO, Sawyerr HO. A Deep Dive into the Review of National Environmental Standards and Regulations Enforcement Agency (NESREA) Act. International Research Journal of Applied Sciences. 2019;1(4):108–125.
  30. Adedoyin OO, Olalekan RM, Olawale SH, et al. A review of environmental, social and health impact assessment (Eshia) practice in Nigeria: a panacea for sustainable development and decision making. MOJ Public Health. 2020;9(3):81‒87.
  31. Olalekan RM, Oluwatoyin OA, Olawale SH, et al. A Critical Review of Health Impact Assessment: Towards Strengthening the Knowledge of Decision Makers Understand Sustainable Development Goals in the Twenty-First Century: Necessity Today; Essentiality Tomorrow. Research and Advances: Environmental Sciences. 2020a;1:72–84.
  32. Olalekan RM, Oluwatoyin O, Olalekan A. Health Impact Assessment: A tool to Advance the Knowledge of Policy Makers Understand Sustainable Development Goals: A Review. ES Journal of Public Health. 2020b;1(1);1002.
  33. Raimi MO, Omidiji AO, Adeolu TA, et al. An Analysis of Bayelsa State Water Challenges on the Rise and Its Possible Solutions. Acta Scientific Agriculture. 2019c;3(8):110–125.
  34. Hamer M. Gas flaring and its impact on aquatic ecosystems: A review of the literature. Environmental Pollution. 2018;236:169–178.
  35. Raimi MO, Oyeyemi AS, Mcfubara KG, et al. Geochemical Background and Correlation Study of Ground Water Quality in Ebocha-Obrikom of Rivers State, Nigeria. Trends Appl Sci Res. 2023;18(1):149–168.
  36. Morufu OR, Tonye VO, Adedoyin OO. Creating the Healthiest Nation: Climate Change and Environmental Health Impacts in Nigeria: A Narrative Review. Scholink Sustainability in Environment. 2021b;6(1).
  37. Okoyen E, Raimi MO, Omidiji AO, et al. Governing the Environmental Impact of Dredging: Consequences for Marine Biodiversity in the Niger Delta Region of Nigeria. Insights Mining Science and technology. 2020;2(3):555586.
  38. Kader S, Raimi MO, Spalevic V, et al. A Concise Study on Essential Parameters for the Sustainability of Lagoon Waters in Terms of Scientific Literature. Preprints. 2023a;2023030099.
  39. Kader S, Raimi MO, Spalevic V, et al. "A concise study on essential parameters for the sustainability of Lagoon waters in terms of scientific literature". Turkish Journal of Agriculture and Forestry: 2023b;47(3).
  40. Glory R, Sylvester CI, Morufu OR, et al. Public and environmental health implications of artisanal petroleum refining and risk reduction strategies in the Niger Delta region of Nigeria. Journal of Biological Research & Biotechnology. 2023;21(1):1836–1851.
  41. Raheem WB, Fadina OO, Idowu OO, et al. The Application of Biomaterials in Ecological Remediation of Land Pollution: Bioremediation of Heavy Metals in Cement Contaminated Soil Using White-Rot Fungus Pleurotus sajor-caju, 11 January 2023, PREPRINT (Version 1) available at Research Square. 2023.
  42. Rauf YO, Raimi MO. Wastes, Wastes, Everywhere Not A Place to Breathe: Redressing and Undressing Ilorin and Yenagoa City. AfricArXiv. 2023.
  43. Akayinaboderi AE, Tano DA, Okoro E. World Environment Day 2024 Initiatives in Bayelsa State: Promoting Environmental Stewardship and Sustainable Practices - A Collaboration Between Federal University Otuoke, Niger Delta University, and the Nigerian Environmental Society. Sustainability in Environment. 2024a;10(1):2025.
  44. Akayinaboderi AE, Tano DA, Okoro E. World Environment Day 2024 Initiatives in Bayelsa State: Promoting Environmental Stewardship and Sustainable Practices - A Collaboration Between Federal University Otuoke, Niger Delta University, and the Nigerian Environmental Society. 2024b;15:2024.
  45. Raimi MO, Adeolu AT, Enabulele CE, et al. Assessment of Air Quality Indices and its Health Impacts in Ilorin Metropolis, Kwara State, Nigeria. Science Park Journals of Scientific Research and Impact. 2018;4(4):060–074.
  46. Morufu Raimi, Clinton Ezekwe. Assessment of Trace Elements in Surface and Ground Water Quality (2017) LAP Lambert Academic Publishing. Mauritius. 2017.
  47. Raimi MO, Sabinus CE. Influence of Organic Amendment on Microbial Activities and Growth of Pepper Cultured on Crude Oil Contaminated Niger Delta Soil. International Journal of Economy, Energy and Environment. 2017;2(4):56–76.
  48. Olalekan RM, Vivien OT, Adedoyin OO, et al. The sources of water supply, sanitation facilities and hygiene practices in oil producing communities in central senatorial district of Bayelsa state, Nigeria. MOJ Public Health. 2018;7(6):337‒345.
  49. Odipe OE, Raimi MO, Suleiman F. Assessment of Heavy Metals in Effluent Water Discharges from Textile Industry and River Water at Close Proximity: A Comparison of Two Textile Industries from Funtua and Zaria, North Western Nigeria. Madridge Journal of Agriculture and Environmental Sciences. 2018;1(1):1–6.
  50. Gift A, Olalekan RM. Access to electricity and water in Nigeria: a panacea to slow the spread of Covid-19. Open Access J Sci. 2020;4(2):34.
  51. Afolabi AS, Raimi MO. When Water Turns Deadly: Investigating Source Identification and Quality of Drinking Water in Piwoyi Community of Federal Capital Territory, Abuja Nigeria. Online Journal of Chemistry. 2021;1:38–58.
  52. Olalekan MR, Olawale HS, Clinton IE. Quality Water, Not Everywhere: Assessing the Hydrogeochemistry of Water Quality across Ebocha-Obrikom Oil and Gas Flaring Area in the Core Niger Delta Region of Nigeria. Pollution. 2022b;8(3):751–778.
  53. Raimi M, Sawyerr H. Preliminary Study of Groundwater Quality Using Hierarchical Classification Approaches for Contaminated Sites in Indigenous Communities Associated with Crude Oil Exploration Facilities in Rivers State, Nigeria. Open Journal of Yangtze Oil and Gas. 2022;7:124–148.
  54. Raimi MO, Sawyerr HO, Ezekwe IC. Toxicants in Water: Hydrochemical Appraisal of Toxic Metals Concentration and Seasonal Variation in Drinking Water Quality in Oil and Gas Field Area of Rivers State, Nigeria. In: PH Saleh, et al. editors. Heavy Metals - New Insights [Working Title]. IntechOpen. 2022a.
  55. Raimi O, Ezekwe C, Bowale A, Samson T. Hydrogeochemical and Multivariate Statistical Techniques to Trace the Sources of Ground Water Contaminants and Affecting Factors of Groundwater Pollution in an Oil and Gas Producing Wetland in Rivers State, Nigeria. Open Journal of Yangtze Oil and Gas. 2022b;7:166–202.
  56. Raimi OM, Sawyerr OH, Ezekwe CI, et al. Many oil wells, one evil: comprehensive assessment of toxic metals concentration, seasonal variation and human health risk in drinking water quality in areas surrounding crude oil exploration facilities in rivers state, Nigeria. Int J Hydro. 2022c;6(1):23‒42.
  57. Olalekan AS, Adewoye SO, Sawyerr OH, et al. Comparative Assessment of Seasonal Variations in the Quality of Surface Water and Its Associated Health Hazards in Gold Mining Areas of Osun State, South-West Nigeria. Adv Environ Eng Res. 2023;4(1):011.
  58. Awogbami SO, Ogunyemi O, Adebayo PA. Protecting the Health of Black Communities: Assessing the Impact of Environmental Hazards from Gold Mining Activities on Health Outcomes among Residents of Osun State, Nigeria. JMIR Preprints. 2024.
  59. Raimi MO, Bilewu OO, Adio ZO, et al. Women Contributions to Sustainable Environments in Nigeria. Journal of Scientific Research in Allied Sciences. 2019a;5(4):35–51.
  60. Raimi MO, Suleiman RM, Odipe OE, et al. Women Role in Environmental Conservation and Development in Nigeria. Ecology & Conservation Science. 2019b;1(2).
  61. Olalekan MR, Abiola I, Ogah A, et al. Exploring How Human Activities Disturb the Balance of Biogeochemical Cycles: Evidence from the Carbon, Nitrogen and Hydrologic Cycles. Research on World Agricultural Economy. 2021;02(03).
  62. Raimi MO, Abiola OS, Atoyebi B. The Challenges and Conservation Strategies of Biodiversity: The Role of Government and Non-Governmental Organization for Action and Results on the Ground. In: Chibueze Izah S editor. Biodiversity in Africa: Potentials, Threats, and Conservation. Sustainable Development and Biodiversity, vol 29. Springer, Singapore. 2022d.
  63. Raimi MO, Austin-AI, Olawale HS, et al. Leaving No One Behind: Impact of Soil Pollution on Biodiversity in the Global South: A Global Call for Action. In: Chibueze Izah S editor. Biodiversity in Africa: Potentials, Threats and Conservation. Sustainable Development and Biodiversity, vol 29. Springer, Singapore. 2022e.
  64. Dienye HE, Ikwuemesi JC, Akankali JO. Gas Flaring-Induced Impacts on Aquatic Resources in the Niger Delta Region, Nigeria. Journal of Aquatic Sciences. 2023;38(1):59–75.
  65. Saliu AO, Komolafe OO, Bamidele CO, et al. The Value of Biodiversity to Sustainable Development in Africa. Sustainable Utilization and Conservation of Africa’s Biological Resources and Environment. 2023;269–294.
  66. Okonkwo CR. Gas Flaring and its Impact on Agriculture and Vegetation in Niger Delta Region of Nigeria. Journal of Environmental Protection. 2017;8(07):715–725.
  67. Ajayi FA, Raimi MO, Steve-Awogbami OC, et al. Policy Responses to Addressing the Issues of Environmental Health Impacts of Charcoal Factory in Nigeria: Necessity Today; Essentiality Tomorrow. Communication, Society and Media. 2020;3(3).
  68. Kabiru M, Umar S, Doe J. Assessment of air quality and health impacts of gas flaring in Niger Delta, Nigeria. Environmental Science and Pollution Research. 2020;27(8):8049–8061.
  69. Nriagu JO. Gas flaring and public health in the Niger Delta, Nigeria. Environmental Research. 2018;160:92–99.
  70. Adedeji OB, Adetunji VE. Aquatic pollution in Nigeria: The way forward. Advances in Environmental Biology. 2011;5(8):2024–2032.
  71. Adedeji OH, Akintoye RA, Olukunle GO. Polycyclic aromatic hydrocarbons and heavy metals in fish from the Niger Delta, Nigeria: A human health risk assessment. Environmental Pollution. 2017;230:642–652.
  72. Davies OA, Kwen K. Status and constraints of artisanal fishers in the Lower Taylor Creek Area, Niger Delta, Nigeria. Journal of Aquatic Sciences. 2013;28(1):1–8.
  73. Kwen K, Nwabeze GO. Economic analysis and status of smoked freshwater clam (Galatea paradoxa) marketing in three selected communities in Yenagoa Local Government Area of Bayelsa State. International Journal of Advancement in Biological Science. 2014;6(1):70–76.
  74. Aghoghovwia OA, Iluma UG, Kwen K, et al. Gillnet fisheries around Polaku and Koroama communities in the lower Taylor creek, Bayelsa state, Nigeria. International Journal of Fisheries and Aquatic Studies. 2022;10(1):01–08.
  75. Odubo TR, Anele KA. Artisanal Crude Oil Refining and Livelihood Adaptive Strategies in theNiger Delta Region. International Journal of Innovative Human Ecology & Nature Studies. 2019a;7(4):20–30.
  76. Odubo TR. Artisanal Crude Oil Refining and Livelihoods in Selected Communities in the Niger Delta Region, Nigeria. PhD Thesis, Department of Sociology, Faculty of Social Sciences, University of Portharcourt, Rivers State, Nigeria.
  77. Raimi MO, Odubo TR, Ogah A. Women, Water and Development in the Global South. Oral Presentation Presented at the Multidisciplinary International Conference on Water in Africa (ICWA 2022) on the theme: Towards Successful Delivery of SDGs 3 & 6, which held February 09 – 11, 2022f.
  78. Raimi MO, Odubo TR, Odubo TV, et al. Gender and Sustainability in the Niger Delta. Oral Presentation Presented at the Multidisciplinary International Conference on Water in Africa (ICWA 2022) on the theme: Towards Successful Delivery of SDGs 3 & 6, which held February 09 – 11, 2022g.
  79. Tagago TA, Ahmed YB. Fishing gear survey of Tatabu floodplain. 2011;109–116.
  80. Omohimoria CU, Oseh JO, Idowu KA. The Effect of Georesources Exploitation on Fishing and Farming in the Niger Delta Region of Nigeria. International Journal of Agriculture Innovations and Research. 2014;3(3):770–781.
  81. Ubani EC, Onyejekwe IM. Environmental impact analysis of gas flaring in the Niger delta region of Nigeria. American J. of Scientific and Industrial Research. 2013;4(2):246–252.
  82. Kindzierski WD. “Importance of human environmental exposure to hazardous air pollutants from gas flares,” Environmental Reviews. 2023;8;41–62.
  83. Ozogu-Agbe N, Chukwurah NC, Muhammed ZA, et al. Negative Effects of Gas Flaring in Niger Delta, Nigeria: Case Study, Oporoma. International Journal of Academic Engineering Research (IJAER). 2020;4(10):32–39.
  84. Gift RA, Olalekan RM, Owobi OE, et al. Nigerians crying for availability of electricity and water: a key driver to life coping measures for deepening stay at home inclusion to slow covid-19 spread. Open Access J Sci. 2020;4(3):69‒80.
  85. Effiong SA, Etowa UE. Oil Spillage Cost, Gas Flaring Cost and Life Expectancy Rate of the Niger Delta People of Nigeria, Advances in Management & Applied Economics. 2012;2(2):211–228.
  86. Arowolo AA, Adaja IJ. Trends of Natural Gas Exploitation in Nigeria and the Implications on the Socio-Economic Stability and Governance. In 35th Nigerian Statistical Association Annual Conference.
  87. Osuagwu SE, Olaifa E. Effects of oil spills on fish production in the Niger Delta. PLoS ONE. 2018;1–14.
  88. Bayode OJA, Adewunmi EA, Odunwole S. Environmental implications of oil exploration and exploitation in the coastal region of Ondo State, Nigeria: A regional planning appraisal. Journal of Geography and Regional Planning. 2011;4(3):110–121.
  89. Henry OS, Odipe EO, Olawale SA. Bacteriological Assessment of Selected Hand Dug Wells in Students’ Residential Area: A Case Study of Osun State College of Health Technology, Ilesa, Nigeria. Global Scientific Journal. 2019;7(1).
  90. Biney, Christian A. The impact of gas flaring on water quality and aquatic ecosystems in the Niger Delta. Environmental Monitoring and Assessment. 2019;191(8):504–512.
  91. Ayibatonyo MN, Ilemi JS, Igoniama EG, et al. Fecundity Estimation of Atlantic mudskipper Periophthalmus barbarus in Ogbo-Okolo mangrove Forest of Santa Barbara River, Bayelsa State Niger Delta, Nigeria. bioRxiv 2024.02.01.578404. 2024a.
  92. Ayibatonyo MN, Bob-Manuel Faye-Ofori G, Morufu OR. Food and Feeding of Atlantic Mudskipper Periophthalmus Barbarus in Ogbo-Okolo Mangrove Forest of Santa Barbara River, Bayelsa State Niger Delta, Nigeria. Qeios. 2024b.
  93. Olalekan RM, Omidiji AO, Williams EA, et al. The roles of all tiers of government and development partners in environmental conservation of natural resource: a case study in Nigeria. MOJ Ecology & Environ Sci. 2019b;4(3):114‒121.
  94. Olalekan RM, Adedoyin OO, Ayibatonbira A, et al. “Digging deeper” evidence on water crisis and its solution in Nigeria for Bayelsa state: a study of current scenario. Int J Hydro. 2019c;3(4):244‒257.
  95. Chijioke, Onuoha B, Ebong, et al. The Impact of Oil Exploration and Environmental Degradation in the Niger Delta Region of Nigeria: A Study of Oil Producing Communities in Akwa Ibom State. Global Journal of Human Social Science, Geo-Sciences, Environmental Disaster Management. 2018;18(3).
  96. Ana GREE, Sridhar MKC, Bamgboye EA. Environmental risk factors and health outcomes in selected communities of the Niger delta area, Perspect Public Health. 2009;129(4):183–191.
  97. Adewale OO, Mustapha U. The Impact of Gas Flaring in Nigeria. International Journal of Science, Technology and Society. 2015;3(2):40–50.
  98. Deinkuro NS, Charles WK, Raimi MO, et al. Environmental Fate of Toxic Volatile Organics from Oil Spills in the Niger Delta Region, Nigeria. International Journal of Environment, Engineering and Education. 2021b;3(3):89–101.
  99. https://earthjournalism.net/stories/gas-flaring-in-the-niger-delta-harming-health-climate-and-environment.
  100. Kwen K, Davies OA, Binyotubo TI. Survey of Fishing Gears and Status of Fishers in Igbedi Creek, Niger Delta, Nigeria. International Journal of Scientific Research in Knowledge. 2013;;1(11):493–501.
  101. Nriagu JO. Oil Industry and the Health of Communities in the Niger Delta of Nigeria, Encyclopedia of Environmental Health. 2011;240–250.
  102. Odubo TV, Obafemi AA, Emenike GC. Analysis of Women’s Participation in Agriculture in Selected States in Niger Delta, Nigeria. International Journal of Innovative Social Sciences & Humanities Research. 2021;7(2):51–61.
  103. Odubo TV. “Analysis of the Role and Participation of Rural Ijaw Women in Agriculture in Niger Delta, Nigeria.’’ PhD Thesis, Department of Geography and Environmental Management University of Port Harcourt, Rivers State, Nigeria. 2019a. p. 159.
  104. Olalekan AS, Adewoye SO, Henry SO, et al. Comprehensive understanding of hydrogeochemical evaluation of seasonal variability in groundwater quality dynamics in the gold mining areas of Osun state, Nigeria. Int J Hydro. 2023;7(5):206‒220.
  105. Olalekan MR, Albert O, Iyingiala AA, et al. An environmental/scientific report into the crude oil spillage incidence in Tein community, Biseni, Bayelsa state Nigeria. J Environ Chem Toxicol. 2022a;6(4):01–06.
  106. Olalekan RM, Dodeye EO, Efegbere HA, et al. Leaving No One Behind? Drinking-Water Challenge on the Rise in Niger Delta Region of Nigeria: A Review. Merit Research Journal of Environmental Science and Toxicology. 2020;6(1):031–049.
  107. Raimi MO, Ezekwe IC, Agusomu TD, et al. Institutional Framework for Methane Emissions Reduction in Nigeria: Policy Insights and Implementation Strategies. JMIR Preprints. 2024.
  108. Raimi MO, Odubo TR. Dutch Diseases and Resources Curse: Key Regulatory Challenges and Opportunities Associated with Extractive Industries in Nigeria. 8th National Conference on Political Stability, Security and Economic Development. Merit House, Abuja-Nigeria. 21st - 22nd July 2022.
  109. Raimi OM, Samson TK, Sunday AB, et al. Air of Uncertainty from Pollution Profiteers: Status of Ambient Air Quality of Sawmill Industry in Ilorin Metropolis, Kwara State, Nigeria. Research Journal of Ecology and Environmental Sciences. 2021;1(1):17–38.
  110. Raimi MO, Clinton IE, Olawale HS. Problematic Groundwater Contaminants: Impact of Surface and Ground Water Quality on the Environment in Ebocha-Obrikom Oil and Gas Producing Area of Rivers State, Nigeria. Oral Presentation Presented at the United Research Forum. 2nd International E-Conference on Geological and Environmental Sustainability during. 2021b.
  111. Raimi MO, Adio ZO, Odipe OE, et al. Impact of Sawmill Industry on Ambient Air Quality: A Case Study of Ilorin Metropolis, Kwara State, Nigeria. Energy and Earth Science. 2020a;3(1).
  112. Raimi MO, Ihuoma BA, Esther OU, et al. “Health Impact Assessment: Expanding Public Policy Tools for Promoting Sustainable Development Goals (SDGs) in Nigeria”. EC Emergency Medicine and Critical Care. 2020c;4(9):2020.
  113. Raimi MO. 21st Century Emerging Issues in Pollution Control. 6th Global Summit and Expo on Pollution Control May 06-07, 2019 Amsterdam, Netherlands.
  114. Raimi MO, Abdulraheem AF, Major I, et al. The Sources of Water Supply, Sanitation Facilities and Hygiene Practices in an Island Community: Amassoma, Bayelsa State, Nigeria. Public Health Open Access. 2019d;3(1):000134.
  115. Raimi MO, Pigha TK, Ochayi EO. Water-Related Problems and Health Conditions in the Oil Producing Communities in Central Senatorial District of Bayelsa State. Imperial Journal of Interdisciplinary Research (IJIR). 2017;3(6).
  116. Raufu YO, Olayinka AS, Raimi MO, et al. Assessment of occupational risks of waste scavenging in Ilorin metropolis. AfricArXiv. 2023.
  117. Jatau SS, Raimi MO, Kakwi JD, et al. Assessing Air Quality at Waste Dump Site of Plateau State University, Bokkos, Nigeria: Evaluating Socio-Economic and Health Implications for the Community. 2024;1–25.
  118. Seiyaboh EI, Izah SC. A Review of Impacts of Gas Flaring on Vegetation and Water Resources in the Niger Delta Region of Nigeria. International Journal of Economy, Energy and Environment. 2017;2(4):48–55.
  119. Izah SC, Ogidi OI, Ogwu MC, et al. Historical Perspectives and Overview of the Value of Herbal Medicine. Herbal Medicine Phytochemistry. 2023;1–33.
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