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Abstract

Nigeria is a heavily polluted country. The problems and challenges of hazardous waste management in Nigeria is enormous. There are enough laws and policies on hazardous waste in Nigeria. There are institutions charged with implementation, execution and enforcing legislation and regulations of hazardous waste in Nigeria. These institutions are not adequately empowered to implement and execute policies or enforce environmental laws. The simple execution of policies on ground and the enforcement of existing laws in the country can improve the environmental situation in Nigeria if environmental institutions are strengthened financially and politically.
Public Health
International
2016; 1(1): 1-5
http://www.sciencepublishinggroup.com/j/phi
doi: 10.11648/j.phi.20160101.11
Review Article
Hazardous Waste Management and Challenges in Nigeria
Edward-Ekpu Douglas Uwagbale
Department of Chemistry, Nasarawa State University, Keffi, Nigeria
Email address:
douglassony@yahoo.com
To cite this article:
Edward-Ekpu Douglas Uwagbale. Hazardous Waste Management and Challenges in Nigeria. Public Health International.
Vol. 1, No. 1, 2016, pp. 1-5. doi: 10.11648/j.phi.20160101.11
Received: September 27, 2016; Accepted: October 8, 2016; Published: October 31, 2016
Abstract: Nigeria is a heavily polluted country. The problems and challenges of hazardous waste management in Nigeria is
enormous. There are enough laws and policies on hazardous waste in Nigeria. There are institutions charged with
implementation, execution and enforcing legislations and regulations of hazardous waste in Nigeria. These institutions are not
adequately empowered to implement and execute policies, or enforce environmental laws. The simple execution of policies on
ground and the enforcement of existing laws in the country can improve the environmental situation in Nigeria if
environmental institutions are strengthened financially and politically.
Keywords: Hazardous Waste, Waste Management, Oil Spillage, Gas flaring, Ogoniland, Nigeria
1. Introduction
According to Central Intelligence Agency [1], Nigeria
covers a total area of about 927,768 km2 with an estimated
population of 181,562,056 people in 2016 and an estimated
growth rate of 2.54% in 2013. Nigeria is most populous
country in Africa. The population is characterized by a strong
rural to urban migration. As at 2010, half of the country’s
population already live in urban areas with estimated annual
urbanisation rate of 3.5% from the year 2010–2015 [1]. The
majority of the urban population lives in large, sprawling
cities in the south like Lagos, Ibadan, Warri, Benin City and
Port Harcourt. Cities of over 5 million people like Kano,
Kaduna and Sokoto also exist in the north. Population
densities, even in rural areas, especially in the southeast part
of the country, are often above 200 persons/km² [2]. The
practical absence of effective regulatory policies, monitoring
system and agency on hazardous waste management and
other environmental issues after independence, made the
country susceptible recipient of exported trans boundary
hazardous waste dump by waste merchants from
industrialized nations. The first recorded incidence was in
1988 when about 4,000 tonnes of toxic waste from Italy was
dumped in Koko port in Nigeria. Prior to 1988, the
government of Nigeria had no meaningful environmental
policy [3]. The government then, in response made the
harmful waste (Special Criminal Provision etc.) Decree 42 of
1988. By this Decree, the Federal government enacted the
Federal Environmental Protection Agency (FEPA) Act which
brought about the creation of the FEPA [4]. However, prior to
an amended by FEPA (Amendment) Decree No. 59 of 1992,
59 industries were established without any Environmental
Impact Assessment (EIA) report. FEPA had to make it
compulsory for all existing industries to carry out
comprehensive environmental audit of plants to the Agency
[5-6]. The concern by the government to protect the
environment gave rise to the creation of the Federal Ministry
of Environment (FMEnv) in 1999 from FEPA, to ensure
effective coordination of all environmental matters [7]. The
ministry oversees agencies including National Oil Spill
Detection and Response Agency (NOSDRA) created in 2006
[8] and National Environmental Standards Regulatory and
Enforcement Agency (NESREA) created in 2007 with
mandates that covers hazardous waste [9]. As a Federation,
environmental regulations in the country concerns the thirty-
six (36) states and the federal capital territory. States are
mainly responsible for their own environmental issues under
various environmental and planning laws. The apex
executive body in Nigeria is the FMEnv with the NESREA as
the main enforcement body [9].
2 Edward-Ekpu Douglas Uwagbale: Hazardous Waste Management and Challenges in Nigeria
2. Hazardous Waste Generation and
Characterization
The 1991 FEPA Guidelines defines hazardous waste as by-
products of society that can pose a substantial hazard to
human health or the environment when improperly managed,
possesses at least one of the four (4) characteristics:
ignitability, corrosivity, reactivity, or toxicity, or appears on
FEPA lists [10]. According to FEPA Act hazardous waste can
be determined by: ignitability; corrosivity; reactivity;
halogenated hydrocarbons concentration; polycyclic aromatic
hydrocarbon (PAH) concentration; polychlorinated Dibenzo
pdioxins and dibenzofurans concentrations; and
polychlorinated Biphenyls (PCB's) concentration [10]. Below
are the major sources of hazardous waste in Nigeria.
Crude Oil Spillage: Petroleum and its derivatives are
highly inflammable and toxic to the ecosystem. The
petroleum and petrochemical industry are the primary base of
Nigeria’s economy and are the major sources of
environmental hazard materials in the country. From 1976 to
1996, there was a total of 4,835 spills in Nigeria resulting in a
cumulative spill volume of 2,382,373.7 barrels of crude oil.
Of this amount only about 15.91% was recovered, on the
average, implying that about 84.09% of the cumulative spill
was lost to the environment [11-12]. In 1980, Texaco Finima-
5 oil blowout in the Niger Delta was curtailed after 30 days
of burning and emission of poisonous gases into the air.
About 200,000 barrels of oil was lost. Four villages including
marine life in the town of Finima and Sangama River were
polluted, leaving 350 hectares of mangroves dead [13].
Another major spillage at Abudu oil pipeline was witnessed
in 1982. The oil flowed into the nearby villages leaving
untold destruction behind. The crops withered, the soil dried
up and marine life died [13]. From 1976 – 1991, 2,796 spills
of about 2.1 million barrels of oil spill was reported in
Ogoniland also in the Niger Delta. This accounts for about 40%
of total oil spills of the Royal Dutch/Shell company [14].
Gas Flaring: It is on record that Nigeria is the highest gas
flarer in the world [15-16]. It has been estimated that the total
emission of carbon dioxide (CO2) from gas flaring in Nigeria
amounts to about 35 million tonnes per year. The average rate
of gas flaring in Nigeria over the period 1970 - 1979 stood at
97%, while for the period 1980 1989, this stood at about
72%, falling marginally to an average of 72% during the
period 1990 2000 [17-18]. The emission of CO2 into the
atmosphere contributes to global warming and the flaring of
natural gas in the Niger delta of the country has led to an
increase in the climatic temperature of gas producing
communities and a destruction of the biotic life in such areas.
Dwelling houses around such sites are bathed in acid rains,
which also leave farmlands wasted and unproductive [19].
Electronic Waste: Waste electrical and electronic
equipment (WEEE) generated in Nigeria sums up to 1.1
million tonnes for 2010, which is around 7 kg per capita [20].
This includes at least 100,000 tonnes of WEEE that entered
the country illegally in 2010. According to Osibanjo and
Nnorom [21], a very significant proportion of ICT users in
Nigeria rely on second-hand equipment from developed
countries, primarily from Europe and North America.
According to M. Amachree [22], these figures have reduced
drastically as a result of the steps taken to monitor the
importation of used EEE into Nigeria and there are presently,
no specific figures. WEEE contains hazardous materials such
as lead, mercury, beryllium, cadmium, and brominated
flame-retardants that pose both human and environmental
health threat [2].
Mining Activities: Crude mining activates expose farm
lands and rivers to toxic chemicals such as lead, sulphur,
arsenic, mercury and cyanide which are threat to humans and
the environment [23]. Mining process in the northern part of
Nigeria result in large amounts of toxic waste. Large amounts
of mine tailings are simply sent into rivers. Most of local
communities in Zamfara state use mercury amalgamation
method in extracting gold, a process particularly degrading
and creates a morass of hazardous waste [24]. The state
suffers environmental exposure to lead from the processing
of lead-rich ore mined by artisans for gold extraction [23].
Exposure to natural radiations emitted by some radioactive
minerals is a major source of health hazards. It has been
established that monazite, pyrochlore and xenotime, which
are obtained as by-products of tin mining in the Jos Plateau,
are radioactive. Mysterious deaths have been attributed to a
high level of radiations released by monazite-rich sand used
for building the houses the deceased lived in in these area
[25].
Household Hazardous Waste: Most household wastes
include among others: household cleaners, materials for
home maintenance, garden products, and automotive
products, the used contents or leftovers of these products, are
either poisonous, toxic, flammable, caustic, corrosive,
reactive, explosive or radioactive, or a combination of these
characteristics [26]. Study by Rosas and Gutiérrez [27]
shows that the quantity of hazardous wastes varies from 0.01-
1% of the total solid municipal wastes, depending on the
characteristics and customs of each locality. Sangodoyin and
Ipadeola, in their study in south western Nigeria reported that
wastes with hazardous components generated by high,
medium and low income earner groups are of 5.6%, 4.4%,
4.2% respectively [28].
Medical Waste: Health-care activities in Nigeria generate
significant amounts of hazardous wastes, such as
chemotherapeutic agents, radio nucleoside, mercury,
anaesthetics gas, corrosive and expired pharmaceuticals.
Used needles, blood stained cotton and expired drugs are
categorised as hazardous medical wastes because they can be
poisonous or toxic [29]. In a study of 5 big health faculties in
Abuja, the average waste generation rate per bed/day was
found to be 2.78 kg of solid waste, 26.5% of the total waste
was hazardous in nature [30]. In a study carried out in the
most populated state in Nigeria (Lagos), the medical wastes
generated range from 0.116 - 0.561 kg/bed/day, while the
total waste is about 215.56 kg/day. Thus, the average
generation rate is approximately 0.181 kg/bed/day [29].
Public Health International 2016; 1(1): 1-5 3
3. Hazardous Waste Management Laws,
Regulations and Conventions
National Legislation, Regulations and Guidelines: The
incidence of Koko waste dump, led to the promulgation of
the harmful waste Special Criminal Provision etc. Decree 42
of 1988, which, made it a criminal act punishable by life
imprisonment, to carry, deposit, transport, import, sell, buy or
negotiate in trade of harmful waste in Nigeria territory. This
was the initial step towards effective management of
hazardous waste in the country [3]. There are existing
legislations, regulations and guidelines for the reduction
and/or elimination of hazards waste generation in Nigeria.
They include: Harmful Waste Act (Decree 42 of 1988)
retained as Cap HI LFN 2004; Environmental Impact
Assessment Act retained as Cap EI2 LFN 2004;
Environmental Guidelines and Standards for the Petroleum
Industry in Nigeria 2002; Petroleum Drilling and production
Regulation 1967; National Environmental Protection
(pollution abatement in industries and factories generating
waste) Regulations S. I. 9 of 1991; National Environmental
Protection; Management of Hazardous Wastes S. I. 15;
Guidelines on Hazardous Chemicals Management;
Guidelines on Pesticides Management; National
Implementation Strategy for Chemicals Hazard
Communication; National Environmental (Mining and
Processing of Coal, Ores and Industrial Minerals)
Regulations, S. I. No. 31 of 2009: National Environmental
(Electrical/Electronic Sector) Regulations, S. I. No. 23 of
2011. Guide for Importers of UEEE.
Economic Policy and Instruments: The country’s policy
includes some good economic instruments as recorded in the
document, A Review of the National Policy On the
Environment [31]. The economic instruments includes: The
Polluter Pays Principle (PPP), which prescribes that the
polluter should bear the cost of preventing, and remediating
pollution; The User Pays Principle (UPP), in which the cost
of a resource to a user must include all the environmental
costs associated with its extraction, transformation and use
(including the costs of alternative or future uses forgone);
The Pollution Prevention Pays Principle (PPPP), which
encourages industries to invest positively to prevent pollution;
promoting tax reliefs and subsidies that encourage
investment in pollution abatement; employing appropriate
insurance and other risk management schemes to fund
remediation and restoration of polluted or degraded areas;
imposing penalty taxes, fines, and charges for noncompliance
with environmental standards and regulations; promoting the
use of market-based extraction charges; and appropriate taxes
on the extraction of resources to discourage their destructive
exploitation and inefficient use [31].
International Conventions: International Conventions
includes Bamako Convention on the Ban of the Import into
Africa and the Control of Trans boundary Movement and
Management of Hazardous Wastes within Africa; Basel
Convention on the Control of Trans boundary Movements of
Hazardous Wastes and their Disposal, including its Ban
Amendment. Basel Convention signatories are required to
obtain written consent of the competent authority before the
movement occurs [32]. Decree No. 42 of 1988 on harmful
waste was harmonized with the Basel Convention [32];
Rotterdam Convention on the Prior Informed Consent
Procedure (PIC) for Certain Chemicals and Pesticides in
International Trade; Stockholm Convention on Persistent
Organic Pollutants (POPs Convention) and Vienna
Convention on the protection of the Ozone Layer and the
Montreal Protocol on substances that Deplete the Ozone layer.
4. Problems and Challenges
WEEE collection in Nigeria is not organised; there are no
collection centres and most times, they are dumped along
with other wastes. A lot of e-waste are also stockpiled in
offices and homes though states such as Lagos have started
stockpiling of e-waste pending the establishment of a
recycling facility. Treatment/Recycling is currently carried
out by the informal sector with no knowledge of the
environmental and health effects of improper e-waste
management [22]. A lot of hazardous, toxic, liquid, solid and
gaseous wastes are produced by Nigerian Agip oil company,
a rich multinational company in oil producing communities
in Ogba/Egbema/Ndoni local government areas of Rivers
State. It is stated in research findings that the company
employ inadequate and below standard disposal strategies
[33], a common situation in Nigeria. In the 8th National
Council on Environment (NEC), non-compliance of
industries and organisations in the oil sector to set standards
and guidelines was noted with dismay. The council noted
with concern that some of the environmental problems in the
country are attributed to non-compliance with the provisions
of EIA Act No. 86 of 1992 [34]. There is also too little effort
from the federal government to enforce compliance
especially when it involves big multinationals as complained
in Memo No. 10 of the 9th NEC Report by the Government of
Bayelsa State. The government drew the attention of the
NEC to the fact that Chevron (Nig) Ltd contravened the EIA
Act by embarking on a drilling project without EIA, and the
consequent environmental damage caused by gas explosion
on its drilling rig, K. S. Endeavour on 16th January, 2012 [35].
Ogoniland was polluted by the Royal Dutch/Shell company
with hazardous waste for 50 years. It took the intervention of
the United Nations Environmental Programme (UNEP) in
2011 before Nigerian government saw the need for action
[36]. But no action was taken till June 2nd, 2016 when
President Buhari officially launched a clean-up programme
[37]. Bassey et al. studied the waste disposal techniques
employed in the management of solid medical wastes in five
(5) selected health facility in Abuja [30]. They found that
medical waste was often mixed with municipal solid waste
and disposed of in residential waste landfills or improper
treatment facilities (e.g. inadequately controlled incinerators).
None of the hospitals surveyed practiced waste segregation.
It was found that 18.3% of the hospitals incinerated waste in
locally built brick incinerator, 9.1% bury their waste, 36.3%
4 Edward-Ekpu Douglas Uwagbale: Hazardous Waste Management and Challenges in Nigeria
burn their waste in open pits, while 36.3% dispose their
waste into municipal dumpsites. It was observed waste
management officers do not have formal training in waste
management techniques and hospital administrators pay very
little attention to appropriate management of medical waste.
Another challenge is the low operating temperatures (~
200 °C) of current medical waste incinerators, resulting in
excess generation of dioxins and furans. Since the location of
these facilities (at hospitals) are usually located in very close
proximity of communities, the emissions from the
incinerators presents a serious health risk to the same
community which the hospital is meant to be serving [38]. In
another study carried out in Port Harcourt, it was found that
hospital wastes were not segregated into marked or colour
coded containers/bins for the different waste streams neither
do they keep records of waste generation and disposal [39].
In an assessment of pharmaceutical waste management in
some Nigerian pharmaceutical industries it was found that
more than 50% of the personnel, supposedly in charge of
waste, were not trained to effectively manage waste. Those
that were trained were either taught just the basics or had
their training many years back and so were not aware of
current trends in hazardous waste management [40]. It was
found that the level of householders’ awareness on the
dangers of Household Hazardous Waste in Enugu metropolis
is low [41].
5. Conclusion
Nigeria has good environmental policy on hazardous waste
and the country is a major player in world environmental
conventions yet the problems and challenges of hazardous
waste management in Nigeria are enormous. This is as a
result of ineffective institutions and lack of political will by
the leaders of the country to enforce laws and execute
policies as seen in the case of Ogoniland. The institutions
charged with implementation, execution and enforcing
legislations and the regulations of hazardous waste in Nigeria
are not adequately empowered to do so. The simple
execution of policies on ground and the enforcement of
already made laws in the country can largely improve the
environmental situation in Nigeria if environmental
institutions are strengthened financially and politically.
References
[1] Central Intelligence Agency (CIA) World Fact Book. 2016
Directorate of Intelligence In
https://www.cia.gov/library/publications/the-world-
factbook/geos/ni.html. Retrieved on September 2nd, 2016.
[2] O. Ogungbuyi, I. C. Nnorom, O. Osibanjo and M. Schluep. E-
Waste Country Assessment Nigeria. E-Waste Africa project of
the secretariat of the Basel Convention. Basel Convention
Coordinating Centre, Nigeria. 2012.
[3] H. Ikhariale. The Koko Incident: The Environment and the
Law, In Shyllon, F (ed) The Law and the Environment in
Nigeria, Ibadan, Vantage Publishers. 1989.
[4] Federal Environmental Protection Agency (FEPA) Act 1988
No. 58.
[5] Federal Environmental Protection Agency (FEPA) Act 1992
No. 59.
[6] M. T. Odubela and I. I. Omoniyi. Compliance Monitoring in
Nigeria’s Industries: 4th International Conference on
Environmental Enforcement, 2001, pp. 123-127.
[7] Federal Environmental Protection Agency (FEPA) Act 1999
No. 14.
[8] National Oil Spill Detection and Response Agency (NOSDRA)
(Establishment) Act, 2006. Federal Republic of Nigeria
Official Gazette, Vol. 93. No. 72, 2006, pp. A407-425.
[9] National Environmental Standards Regulatory and
Enforcement Agency (NESREA). Corporate Strategic Plan:
Building Capacity, Enforcing Compliance. 2009-2012.
[10] Federal Environmental Protection Agency (FEPA). The
National Guidelines and Standards for Environmental
Pollution Control in Nigeria. Federal Environmental
Protection Agency, 1991.
[11] Niger Delta Environmental Survey (NDES). Environment and
Socio-economic Characteristics. Phase 1 Report, Port
Harcourt. 1997.
[12] Nigerian National Petroleum Corporation (NNPC). Annual
Statistical Bulletin, 1997.
[13] V. E. Kalu. Toxic Wastes and The Nigerian Environment: an
appraisal. Department of Private & Property Law University
of Benin, Benin City. 2006.
[14] S. Crayford. Conflict and conflict resolution in Africa. Africa
today. Vol. 42, No. 2, 1996, pp. 183-197.
[15] World Bank. Defining an Environmental Development
Strategy for the Niger Delta. Vol. 2, 1995. Industry and
Energy Operations Division (West Central Africa Department).
Washington D. C.
[16] World Bank. World Development Report, 2000/2001. Industry
and Energy Operations Division (West Central Africa
Department). Washington D. C.
[17] Central Bank of Nigeria (CBN). Central Bank of Nigeria,
Statistical Bulletin, and Annual Report, 1998, Abuja, Nigeria
[18] Central Bank of Nigeria (CBN). Statement of Accounts, 2000.
CBN. Abuja, Nigeria
[19] Newswatch Magazine, Vol. 14, June 26. 1988. pp. 29.
[20] Y. Amoyaw-Osei, O. O. Agyekum, J. A. Pwamang, E. Mueller,
R. Fasko, and M. Schluep. Ghana E-Waste Country
Assessment: report of component 1&2 of the UNEP SBC e-
waste Africa project for Ghana. Accra, Ghana. Green
Advocacy, Ghana & Empa, Switzerland. 2011.
[21] O. Osibanjo and I. C. Nnorom. The challenge of electronic
waste e-waste management in developing countries. Waste
Manage Res Vol. 25, 2007, pp. 489–501.
[22] M. Amachree. Update on E-Waste Management in Nigeria: a
presentation made at the 3rd annual meeting of the Global E-
waste Management Network (GEM3). San Francisco, USA.
15th- 19th, 2013
Public Health International 2016; 1(1): 1-5 5
[23] M. O. Aremu, G. N. Ozonyia and P. P. Ikokoh, Electronic
journal of Environmental Agricultural and Food Chemistry.
Vol. 10, No. 6, 2011, pp. 2296-2304.
[24] A. I. Rasheed and A. K Amuda. Impacts of Artisanal Mining
on Some Heavy Metals Concentration in Surface Water in
Kutcheri, Zamfara State North-Western Nigeria. Academic
Journal of Interdisciplinary Studies. Vol. 3, No. 7, 2014, pp.
74-82.
[25] I. N. Aigbedion. Environmental Pollution in the Niger-Delta,
Nigeria. Inter-Discplinary J. Vol 3, No. 4, 2005, pp. 205–210.
[26] P. Agamuthu. Solid Waste: Principles and Management. 2001.
Institute of Biological Sciences, University of Malaya.
[27] D. A. Rosas and G. P. Constantino. Study of generation of
household hazardous waste in a residential area. 1998.
National Autonomous University of Mexico School of
Engineering. Estudio degeneraciónde residuos peligrosos
domésticos en una zona habitacional. 1998. Universidad
Nacional Autónoma de México Facultad de Ingeniería.
[28] A. Y. Sangodoyin and S. F. Ipadeola. Hazardous Wastes:
Assessing the Efficacy of Structures and Approaches to
Management in Nigeria. Environmental Management and
Health. Vol. 11, No. 1, 2000, pp. 39- 46.
[29] O. Awodele, A. A. Adewoye and A. C. Oparah. Assessment of
Medical Waste Management in Seven Hospitals in Lagos,
Nigeria. BMC Public Health. Vol. 16, 2016, pp. 269.
[30] B. E. Bassey, M. O. Benka-Coker and H. S. Aluyi. A
Characterization and management of solid medical wastes in
the Federal Capital Territory, Abuja Nigeria. African Health
Sciences. Vol. 6, No. 1, 2006, pp. 58-63.
[31] Federal Ministry of Environment (FMEnv.) A Review of the
National Policy On the Environment, 1999. In
http://environment.gov.ng/index.php/downloads/ Retrieved on
September 2nd, 2016
[32] Basel Convention Country Fact Sheet, Nigeria. In
www.basel.int Retrieved on September 2nd, 2016.
[33] G. A. Wokocha. Impacts of industrial wastes disposal
strategies on oil producing communities in Rivers State,
Nigeria. Journal of Natural Sciences Research. Vol. 4, No. 22,
2014, 159-163.
[34] National Council On Environment (NEC). Transforming the
Nigerian Environment. 8t h National Council On Environment
Report. 26th – 30th September, 2011. FMEnv.
[35] National Council On Environment (NEC). Green Economy - A
Panacea for Sustainable Development. 9th National Council
On Environment Report. 5th – 10th May, 2013. FMEnv.
[36] United Nation Environmental Programme. UNEP Welcomes
Nigerian Government’s Green Light for Ogoniland Oil Clean-
up. UNEP News Centre August 1st, 2012.
[37] Vanguard Newspaper. Buhari Lunches Clean-Up of Ogoniland
Today. June 2nd, 2016. In
www.vanguardngr.com/2016/06/buhari-lunches-clean-
ogoniland-today
[38] BCRCCATTT. Report of Regional Workshop On Successful
Case Studies of Recycling, Reuse and Resource Recovery
Methods Towards the Environmentally Sound Management
(ESM) Of Hazardous Wastes in Africa, Conference Centre,
University of Ibadan, Ibadan, Nigeria. 9th –12th August 2004.
[39] D. N. Ogbonna. A. Chindah and N. Ubani. Waste management
options for health care wastes in Nigeria: a case study of Port
Harcourt hospitals. Journal of Public Health and
Epidemiology. Vol. 4, No. 6, 2012, pp. 156-169.
[40] N. C. Ngwuluka, N. A. Ochekpe and P. O. Odumosu. An
assessment of pharmaceutical waste management in some
Nigerian pharmaceutical industries. African Journal of
Biotechnology. Vol. 10, No. 54, 2011, pp. 11259-11264.
[41] N. N. Ubachukwu, P. O. Phil-Eze and C. N. Emeribe. Analysis
of Household Hazardous Wastes Awareness Level in Enugu
Metropolis. Academic Journal of Interdisciplinary Studies,
Vol. 3, No. 1, 2014, pp. 369-377.
... Firstly, the persistent release of harmful gases into the Ekpan community from industrial activities has become a thing of concern. These gases are continuously flared all-day e.g., carbon dioxide, methane, propane, ethane, etc., which accumulate into major environmental hazards such as climate change, global warming, acid rain, infertile soil, health-related problems such as infertility, constant headaches, eye diseases, cardiovascular and respiratory diseases, etc. Inadequate facilities for proper management of harmful/waste also contribute to the increase in gas flaring [13,14]. No appropriate law has been given by the government against this act, and the ones given out are not monitored properly. ...
... But the wet season value was within the FMENV drinking water limit. These findings support the views of [13,14] on the presence of acid rain in Nigeria and the root causes being the irrational flaring of gas. ...
... Comparison of results with FMENV and DPR standards[12,13]. ...
Article
Full-text available
In the Ekpan settlement of the Uvwie local government area, Delta state, Nigeria, a study on gas flaring and its effects on the environment was carried out. It was found that hazardous gases have been released into the environment because of air pollution caused by the combustion of methane and other hazardous flue gases during the manufacturing and processing of hydrocarbons. Industrial flue gas flare-ups cause several problems and are harmful to public health and the environment. This study investigated the pH of rainwater, as well as air pollutants (NO2, SO2, CO2, CO, and suspended particle matter). During the dry and wet seasons, samples of air and rainwater were collected at different distances around exposure sites, and they were then examined using established techniques for the air contaminants. Descriptive statistical tools such as mean and standard deviation were used to analyze the variance and degree of effect of pollutants. The obtained results showed that the mean CO2 concentrations in the dry and wet seasons were, respectively, 0.036 ppm and 0.26 ppm and that the pH of rainwater in the wet season was 6.82, both of which were within the safe limits, indicating that there were little to no negative effects on the environment. However, the average concentrations of suspended particulate matter in dry and wet seasons respectively were 7.92 mg/m3 and 5.95 mg/m3, NO2 was 0.15ppm and 0.10ppm, SO2 was 0.72ppm and 0.10ppm, CO was 11.20ppm and 10.24ppm, and CO2 0.036ppm and 0.26ppm. The pH of rainwater was 6.02 for the dry season which exceeded the acceptable ambient air limits set by the DPR (2002) and FMENV (1991), while during the wet season, the pH was 6.82. This study suggested that the activity of continuous gas flaring is one of the main causes of high concentrations of these air pollutants within the examined community. The findings further suggested that the numerous environmental, socioeconomic, and political issues within Epkan were linked to the effects of gas flaring. This study suggests that the challenges caused by gas flares for the Ekpan community are good enough grounds to stop the practice of gas flaring in the area and the government needs to enact strict legislation with penalties for defaulters. The study finally recommended that flared gas could be refined and reused.
... Firstly, the persistent release of harmful gases into the Ekpan community from industrial activities has become a thing of concern. These gases are continuously flared all-day e.g., carbon dioxide, methane, propane, ethane, etc., which accumulate into major environmental hazards such as climate change, global warming, acid rain, infertile soil, health-related problems such as infertility, constant headaches, eye diseases, cardiovascular and respiratory diseases, etc. Inadequate facilities for proper management of harmful/waste also contribute to the increase in gas flaring [13,14]. No appropriate law has been given by the government against this act, and the ones given out are not monitored properly. ...
... But the wet season value was within the FMENV drinking water limit. These findings support the views of [13,14] on the presence of acid rain in Nigeria and the root causes being the irrational flaring of gas. ...
... Comparison of results with FMENV and DPR standards[12,13]. ...
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In the Ekpan settlement of the Uvwie local government area, Delta state, Nigeria, a study on gas flaring and its effects on the environment was carried out. It was found that hazardous gases have been released into the environment because of air pollution caused by the combustion of methane and other hazardous flue gases during the manufacturing and processing of hydrocarbons. Industrial flue gas flare-ups cause several problems and are harmful to public health and the environment. This study investigated the pH of rainwater, as well as air pollutants (NO2, SO2, CO2, CO, and suspended particle matter). During the dry and wet seasons, samples of air and rainwater were collected at different distances around exposure sites, and they were then examined using established techniques for the air contaminants. Descriptive statistical tools such as mean and standard deviation were used to analyze the variance and degree of effect of pollutants. The obtained results showed that the mean CO2 concentrations in the dry and wet seasons were, respectively, 0.036 ppm and 0.26 ppm and that the pH of rainwater in the wet season was 6.82, both of which were within the safe limits, indicating that there were little to no negative effects on the environment. However, the average concentrations of suspended particulate matter in dry and wet seasons respectively were 7.92 mg/m3 and 5.95 mg/m3, NO2 was 0.15ppm and 0.10ppm, SO2 was 0.72ppm and 0.10ppm, CO was 11.20ppm and 10.24ppm, and CO2 0.036ppm and 0.26ppm. The pH of rainwater was 6.02 for the dry season which exceeded the acceptable ambient air limits set by the DPR (2002) and FMENV (1991), while during the wet season, the pH was 6.82. This study suggested that the activity of continuous gas flaring is one of the main causes of high concentrations of these air pollutants within the examined community. The findings further suggested that the numerous environmental, socioeconomic, and political issues within Epkan were linked to the effects of gas flaring. This study suggests that the challenges caused by gas flares for the Ekpan community are good enough grounds to stop the practice of gas flaring in the area and the government needs to enact strict legislation with penalties for defaulters. The study finally recommended that flared gas could be refined and reused.
... Concentration of hazardous waste would be classified as 'special waste' and as such would be subject to the Special Waste Regulations 1996 with its consequent regulation of storage, transport, handling and treatment (Yusuf, 2009). However, environmentally sound management of hazardous wastes in Nigeria is faced with multiple challenges that include: inadequate information and statistics on the quantity and sources of hazardous waste generated in the country (Ubachukwu et al., 2014); lack of public awareness on the nature of hazardous waste and the danger posed to public health and the environment (Uwagbale, 2016); lack of political will by the government to put in place and enforce adequate legislations to deal explicitly with the matter of hazardous waste management, and inadequate training and capacity building on the current trends in the area of hazardous waste management (Ngwuluka et al., 2011). ...
... Crude Oil Spillage: The major sources of hazardous materials in Nigeria environmental are petrochemical industries. From 1976-1996 alone, there were a total of 4,835 oil spills that resulted in a spill volume of about 2.3 million barrels of crude oil (Kalu, 2006;Uwagbale, 2016). ...
... Major household wastes include the following: household cleaners and adhesives, automotive products, materials for home maintenance and garden products. The remains of these products are either found to be fatal, toxic, caustic, corrosive, flammable, reactive, explosive, radioactive or a combination of these (Agamuthu, 2001;Uwagbale, 2016). ...
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Hazardous wastes are substances that are no longer needed and have no current or perceived value at a given time or place. Many of the materials used or produced in chemical processes possess hazardous properties. The key hazardous wastes sources include industrial, medical, and household wastes, and occur in solid, liquid, or gaseous states. These are wastes that are classified and/or have intrinsic or inbuilt chemical and physical distinctiveness of toxicity, ignitability, corrosivity, and reactivity. Managing hazardous wastes is of immense significance to human, economic, social and environmental health conditions. Hazardous wastes management practice in Nigeria is not in consonance with the best global practices. Many hazardous wastes are dumped indiscriminately, which constitutes hazard to the environment and posed public health concerns. This study analysed the strength, weaknesses, opportunities and threats of hazardous wastes management in Nigeria. There are various environmental regulations on hazardous wastes in the country, but implementation remains a challenge, as such there is need for more proactive measures to be taken towards sustainable solutions to the problems.
... It is common knowledge that heavy metals are naturally occurring elements on the earth's crust. However, environmental contamination and subsequent exposure to humans result from several anthropogenic activities such as tanning, mining, electroplating, smelting, and domestic and agricultural uses of compounds containing these metals [8]. Many of these heavy metals are toxic at deficient concentrations; arsenic (As), cadmium (Cd), chromium (Cr), copper (Cu), lead (Pb), mercury (Hg), nickel (Ni), selenium (Se), silver (Ag) and zinc (Zn) are cytotoxic, carcinogenic, and mutagenic [9]. ...
... All these toxic wastes are sent indiscriminately into the water bodies such as lakes, rivers and seas without treatment. Uwagbale [61] reported that Nigeria petroleum and petrochemical industry recovered about 15.91% of the total cumulative spill volume (2,382,373.7 barrels) of crude oil between 1976 and 1996 while about 84.09% was lost into the environment. Furthermore, in-between 1976 and 1991, in Ogoniland, Niger Delta region of Nigeria, about 2,100,000 barrels of oil spill was reported. ...
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Biomass and wastes are increasingly being used as major energy sources not only in Nigeria but also worldwide. Different wastes/biomass to energy technologies have been used in the past by several researchers but anaerobic digestion happens to be the best option due to its eco-friendliness and simplicity of its design. There are huge amounts of wastes generated from agriculture, municipalities and industries both in rural Nigeria and urban areas that are being underutilized due to lack of information on their potential for biogas production. Laboratory, pilot and full-scale studies have shown that agricultural, municipal solid and industrial wastes all have potential for bioenergy generation. The potential of bioenergy production from agricultural waste, municipal solid waste (MSW) and industrial waste within the country has been sought in various scientific databases from 1997 to 2020 and related information was obtained. This review article examines the agricultural, municipal solid and industrial wastes found in Nigeria and the biogas production potential from these wastes usable as alternative to fossil fuels. Current trend, recent issues and future prospect of anaerobic digestion are also considered in this article.
... Reference E-waste generation LED lamps Canada Kumar et al., 2019General Nigeria Odeyingbo et al., 2019Nnorom and Osibanjo, 2008;Amori et al., 2013;Sullivan, 2014;Bello et al., 2015;Nnorom and Osibanjo, 2007;Babayemi et al., 2016;Ogbomo et Omole et al., 2015;Babayemi et al., 2017;Adeola and Othman, 2011;Alake and Ighalo, 2012;Omole et al., 2015;Babayemi et al., 2017;Ogbomo et al., 2012;Edward-Ekpu, 2016;Omenogo, 2014;Ijaiya et al., 2018 General;paint and mercury-containing lamps USA Hickle, 2014;Wagner, 2009;Kahhat et al., 2008 Environmental management of e-waste Kang and Schoenung, 2006a;Betts, 2008a;Kang and Schoenung, 2005;Gullett et al., 2007;Kang and Schoenung, 2006aGeneral France Arduin et al., 2017General Canada Kumar and Holuszko, 2016mobile phones Nigeria Terada, 2012;Osuagwu and Ikerinonwu, 2010;Igharo et al., 2014;Nnorom et al., 2009;Terada, 2012 Althaf et al., 2020;Saphores et al., 2006;Smith et al., 2013;Saphores et al., 2012;Milovantseva and Saphores, 2013 General; household appliances Nigeria Umesi and Onyia, 2008;Popoola and Popoola, 2019;Miner et al., 2020;Umaebolu, 2018;Nduneseokwu et al., 2017;Ben-Enukora et al., 2017;Azodo et al., 2017;Onwughara et al., 2010 E-waste problems and challenges General South Africa Grant, 2019 General; ICT equipment and devices Nigeria Adama et al., 2019;Ejiogu, 2013;Adediran and Abdulkarim, 2012;Obaje, 2013;Ukem, 2008;Egwali and Imouokhome, 2013;Eyo, 2008 Ohajinwa et al., 2017;Ogundiran et al., 2014;Ohajinwa et al., 2018 E-waste legislation General; ICT equipment Nigeria Amechi and Oni, 2019;Aborele et al., 2015General UK Powell-Turner et al., 2016Callaghan, 2007 General USA Schumacher andAgbemabiese, 2019;Huisman andMagalini, 2007 General Canada Lepawsky, 2012 are dumped in developing countries resulting in massive pollution, environmental and health problems in local communities (Powell-Turner et al., 2016). The Basel Convention aims to protect human health and the environment against adverse effects resulting from the generation, transboundary movements and management of hazardous wastes and other wastes. ...
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Waste generated from electrical and electronic equipment collectively known as e-waste has remained a persistent environmental problem. Globally, approximately 53.6 million tons of e-waste was generated in 2019. Of this amount generated, less than 13 percent was recycled and the rest ended up in landfills or incinerators creating enormous environmental and health concerns due to the presence of hazardous materials. While there are several previous-studies on e-waste, research findings of the United Nations global e-waste report 2020 shows that many countries are not sufficiently managing e-waste generated and greater effort is urgently required to ensure smarter and more sustainable e-waste management. On this premise, this study critically reviews previous research on e-waste generation and management practices of selected-countries - Canada, France, United States, United Kingdom, Nigeria and South Africa; provides an overview of progress made and identifies areas for improvement. These countries are selected because they are some of the largest-producers of e-waste worldwide. To achieve the objectives of this study, previous-studies from 2005-2020 are collected from databases. The study focuses on aspects such as e-waste generation, e-waste recycling, e-waste disposal methods and behaviour, environmental management of e-waste, e-waste problems/challenges and e-waste legislation of these countries. This study further categorised previous-studies of selected-countries in relation to type and scope of research, e-waste categories evaluated and study locations. Based on the findings/outcomes of the analysis on the current-situation of the selected-countries in the literature, this study proposes generic best-practice approaches to e-waste generation and environmental management taking into account country-specific issues and identifies future research areas.
... While soil and water are considered as some of the most valuable indispensable natural resources that sustain human existence both could also function as channels of diseases transmission if contaminated with toxic pollutants. Oftentimes in Nigeria, large amounts of toxic waste are secretly and illegally disposed into rivers, thereby endangering both aquatic and human lives (Edward-Ekpu 2016). ...
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There is no doubt about the existence of environmental laws at the municipal and international levels. However, the level of compliance and enforcement is a subject for reassessment in view of the recurrent instances of environmental degradation across the world. This has warranted the need for this scholarly inquiry. Employing the doctrinal methodology of legal research (Hutchinson and Duncan, 2013), this study examines selected international legal instruments for the environmental protection of air,water, and soil against pollution.The study also considers the compliance level and enforcement approach of these international instruments at amunicipal level in selected countries.The selection of countries cut across the three continents of Europe, Africa, and Asia respectively.Theobjective is to identify the prospects and challenges associated with the enforcement of environmental laws in these countries, in order to proffer useful suggestions for more sustainablemeans of environmental protection. In light of the above, the study is divided into five sections. First is an introduction to the study, which is followed by an exposition of the concept of “regulation” in environmental protection and enforcement. The next three sections border on global environmental protection and air, soil, and water pollution respectively.The last section is the conclusion.
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