The Land of Electronics: Government Policies

On this last post of “The Land of Electronics”, I will be examining what Nigeria’s government has done to control and regulate the challenge of electronic waste in the informal sector.

In 1988, the exportation of hazardous wastes to developing countries garnered global attention after 3,800 tonnes of toxic wastes were found to be dumped in a dirt lot in Koko, Nigeria, as a deal arranged by an Italian waste trader (Liu, 1992). In response to this incident, the Nigerian Government has subsequently enacted the ‘Harmful Wastes Decree’, which provides a legal framework to regulate the disposal of toxic and hazardous waste into the environment of Nigeria, creating the Federal Environment Protection Agency (FEPA) in the process (Ideho, 2012). Under their National Policy on Environment, Nigeria further states that appropriate agencies are responsible to set up a regional framework and standard to combat against the transboundary movement of hazardous waste, which electronic waste falls under (Ideho, 2012).

However, there are certain significant limitations to this policy that reduce its effectiveness in managing the environmental pollution of electronic waste. Firstly, the hazardous electronic wastes imported into Nigeria are often imported under the ‘guise’ of them being second-hand goods. Furthermore, Amechi and Oni (2019) has found that these ‘second-hand goods’ are brought into Nigeria through used vehicles, of which are not subjected to inspection and control by regulatory agencies as compared to import routes through containers.

Most significantly, the challenge with ridding the country of the  hazardous and polluting electronic wastes derives from the fact that much of the informal Nigerian community depends on the transnational trade of e-waste for their livelihoods. For example, it was found that the formal refurbishing sector in Nigeria provided income to more than 30,000 people (Amechi and Oni, 2019). This suggests that the illegal importation of electronic waste has provided even more jobs for those operating in the informal sectors. Through the importation of these e-wastes, trades such as dismantling, repairing and refurbishing emerge as new opportunities for settlers that are unable to find formal employment.

In hindsight, the challenges of managing electronic waste are more complicated than perceived due to the conflicting socioeconomic benefits that electronic waste trade provides. Furthermore, it can be observed that policies can only do so much to regulate the on-the-ground realities of waste regulation. Through these observations, I believe that in order to truly curb the environmental pollution in these marginalised countries, the accountability lies in the hand of the consumers that make the decision to consume such products and services.

References

Amechi, E.P. & Oni, B.A. (2019) ‘Import of Electronic Waste into Nigeria: the Imperative of a Regulatory Policy Shift’, Chinese Journal of Environmental Law, 3, 141–166.

Ideho, B.A. (2012) E-Waste Management: A Case Study of Lagos State, Nigeria, Master’s Thesis. University of Jyväskylä .

Liu, S. (1992) ‘The Koko Incident: Developing International Norms for the Transboundary Movement of Hazardous Waste’, Journal of Natural Resources & Environmental Law, 8.

The Land of Electronics: Nigeria

In my previous post, I touched on how the disposal of electronic waste has very damaging effects on certain marginalised communities in the world, emphasising the environmental injustice of environmental pollution. Today, I would like to examine the impacts of electronic waste disposal and the subsequent socio-economic impacts of Nigeria.

Nigeria is a major destination of electronic waste, importing over 60,000 tonnes of used electronics and electrical equipment via the ports of Lagos alone (Galan, 2019). After sifting through the electronics and dumping those which are unusable, individuals in the informal sector in Nigeria are then tasked to collect and dismantle the electronics by hand to extract out the sellable components. Many of these dismantlers have reported injuries on their hands and feet from the sharp waste fractions, as well as an inhalation of the cadmium-containing internal phosphorous that is released as dust upon dismantling (Manhart et al., 2011).

The remnants of the e-waste that are deemed unusable are burnt, where ‘over 52,000 tonnes of brominated (flame retardant) plastics, 4,000 tonnes of lead, 80 tonnes of cadmium and 0.3 tonnes of mercury are burned or dumped in Nigeria every year’ (Galan, 2019). Furthermore, the highly acidic pH of 3.4 observed in some water bodies of the industrialised areas of Lagos may accelerate the dissolution and mobility of heavy metals from disposed waste items  toward water bodies used for domestic purposes (Nnorom & Odeyingbo, 2020), creating toxic and hazardous water bodies that endanger the locals who depend on these water bodies for water and sanitation purposes.

The adverse health impacts illustrate the negative social implications that e-waste has on the local community in Nigeria. The unfortunate paradox to this is that the locals are highly dependent on the informal electronic waste sector for their income. As such, this forces them to choose between their health or their income, of which the lack of awareness to these health implications would lead them to choose the latter. The extreme injustice observed here where these communities are systematically coerced into a “suffer now or suffer later” situation highlights the marginalisation of certain communities through environmental pollution, of which consumers hardly see the entirety of the implications of their consumption.

References

Galan, I. (2019) ‘Dark skies, bright future: overcoming Nigeria’s e-waste epidemic’, UNEP. Available at: http://www.unep.org/news-and-stories/story/dark-skies-bright-future-overcoming-nigerias-e-waste-epidemic (accessed February 2022).

Manhart, A., Osibanjo, O., Aderinto, A. & Prakash, S. (2011) Informal e-waste management in Lagos, Nigeria – socio-economic impacts and feasibility of international recycling co-operations , Institute For Applied Ecology.

Nnorom, I.C. & Odeyingbo, O.A. (2020) ‘Electronic waste management practices in Nigeria’, in Handbook of Electronic Waste Management, Elsevier, 323–354.

The Land of Electronics

When I was younger, I had always thought that I was doing the environment a favour as I was saving dozens of trees by using my computer to take notes when I study. Evidently to me, there was a direct relationship between the existence of my computer to the declining usage of paper sheets and paper notebooks. I was definitely saving the world. Right?

Unbeknownst to my naive younger self, I had not heard of electronic pollution. So what is electronic waste pollution?

Electronic waste pollution occurs when electronic waste is dumped in landfills. The marginalisation of pollution effects can be significantly observed here as about 80% of e-waste from developed countries have been and is still continuing to be illegally exported to developing countries such as Nigeria, Ghana and Pakistan (Awasthi, 2015). This suggests that many of the electronics that we have bought, used and eventually ignorantly discarded may have had ended up in landfills in one of the above-mentioned countries.

As these electronic waste often contain hazardous substances such as Copper, Lead, Tin, and Nickel (Adesokan et al., 2016), the disposal of these types of waste become extremely problematic when the toxins from the electronics enter the soil. In a study done on the soil pollution caused by e-waste in Nigeria by Adesokan et al., (2016), it was found that Nigeria receives an estimate of around 40,000 tonnes of e-waste every month, of which, much of these waste are then subjected to environmentally unsound scavenging methods such as the unprotected acid leaching of Printed Wiring Boards (PWBs) and the unprotected dismantling and burning of the electronics to recover precious metals by the informal sector. Through this, the toxins from the burnt metals are released into the soil, air and water from surface runoff (Ahmed, 2016), creating an extremely toxic environment for the informal settlers near these landfills. Song and Li (2015) further found that there were ‘increases in spontaneous abortions, stillbirths, premature births, reduced birth weights and infant lengths in pregnant women exposed to heavy metals from e-waste sites’, illustrating the harmful health implications of e-waste pollution.

Definitely, we as consumers don’t think too much about what happens to our personal items once they’re discarded. Just imagine the number of times we have discarded a perfectly functional phone or laptop because of our consumer mindset to replace it with the next new best model. The idea of using laptops or smartphones as “green” was truly such a misguided opinion, of which consumers like myself should be more accountable for.

Subsequently, the following few posts will go more in-depth into how the challenge of e-waste affect the marginalised groups more significantly and how these groups are handling these environmental challenges.

 

References

Adesokan, M.D., Adie, G.U. & Osibanjo, O. (2016) ‘Soil Pollution by Toxic Metals near E-waste Recycling Operations in Ibadan, Nigeria’, Journal of Health & Pollution, 6, 26–33.

Ahmed, S.F. (2016) ‘The Global Cost of Electronic Waste’, The Atlantic. Available at: https://www.theatlantic.com/technology/archive/2016/09/the-global-cost-of-electronic-waste/502019/ (accessed February 2022).

Awasthi, A.K., Zeng, X. & Li, J. (2016) ‘Environmental pollution of electronic waste recycling in India: A critical review’, Environmental Pollution, 211, 259–270.

Song, Q. & Li, J. (2015) ‘A review on human health consequences of metals exposure to e-waste in China’, Environmental Pollution, 196, 450–461.

Not so Trashy Travelling? Ecotourism in Feynan Ecolodge

 

Hello again! Welcome back to the last post of week 5 and week 6’s theme of Trashy Travelling! This last post will be different from the previous posts as it provides an alternative, more sustainable look to tourism compared to the impacts of tourism that we have seen so far through the lens of Boracay and Mount Everest. The Feynan Ecolodge is an award-winning lodge based in the Wadi Araba area of Dana Biosphere Reserve in Jordan and it was built by the Royal Society for the Conservation of Nature (Namrouqa, 2014). The lodge operates on a model of ecotourism, where the focus of their operations lies in generating revenue to fund conservation and provide sustainable income for the locals in the area, all while ensuring that their environmental footprint is minimised.

A characteristic of the lodge that can be often overlooked but plays a significant role in the lodge’s sustainability is its architecture. Feynan Ecolodge was constructed using earthen materials such as sand and cement as the base and straw bales to ensure low thermal bridging as a form of temperature regulation (Atiyat, 2017). The use of these materials indirectly preserves trees and protects the environment as it reduces the demand for wood and coal to make bricks, of which processing these raw materials releases a significant amount of carbon emissions (Guttikunda, 2015). Furthermore, the cutting down of trees for wood also reduces the amount of carbon sinks in the environment, aggravating the environment even more. Additionally, with the usage of ferro-cement sandwiching straw bales to form the roof to regulate temperature, additional carbon emitting heaters or air-conditioners are not needed, minimising their carbon footprint (Atiyat, 2017). As such, it is evident that the earthen architecture used to construct the lodge plays a significant role in the sustainability of the ecolodge.

Besides the earthen architecture, Feynan Ecolodge does not connect itself to the electricity grid. Rather, the lodge generates 100% of their electricity through solar panels mounted on their roof top. The electricity is then used limitedly for activities deemed necessary such as for lighting or for refrigeration, of which these electrical appliances are certified as greener alternatives. There are no dryers available as the laundry is air dried to reduce electricity consumption. In total, the daily electricity consumption for the lodge is restricted to 16-18 KWhr, less than a typical two bedroom apartment in Amman, Jordan (‘Sustainability’, 2013). The stringent usage of electricity for the lodge illustrates the extent to which the lodge operates to save energy and reduce their environmental footprint.

Definitely, there are many more aspects of the ecolodge that contribute to their sustainable ecotourism that I have not touched on. Nonetheless, it is important to acknowledge the idea of sustainable tourism as not just a dream but rather a feasible and attainable goal with the right steps in place, where the Feynan Ecolodge is a prime example of such an operating model. Linking back to the wider theme of my blog about consumption behaviour on environmental pollution, I believe that besides blaming big operators for the environmental damage of tourism, it is essential for consumers like ourselves to do our parts as well. To encourage more operators to convert their tourism destinations into sites of ecotourism, there needs to be more demand from tourists. In essence, there should be a responsibility placed on travellers and consumers to engage in sustainable tourism practices and engage with operators that follow such a model.

 

References

Atiyat, D.I. (2017) ‘Earthen Architecture: Characteristics and Implementation, Case Study of Earthen Building in Jordan’, Civil Engineering Research Journal, 2.

Guttikunda, S.K. (2014) ‘Emissions from the Brick Manufacturing Industry’, in Dhaka Megacity: Geospatial Perspectives on Urbanisation, Environment and Health, Springer Geography.

Namrouqa , H. (2014) ‘Feynan Eco-lodge announced as finalist in National Geographic’s World Legacy Awards’, Jordan Times. Available at: http://www.jordantimes.com/news/local/feynan-eco-lodge-announced-finalist-national-geographics-world-legacy-awards (accessed February 2022).

‘Sustainability’ (2013) EcoHotels. Available at: https://ecohotels.me/en/feynan/sustainability-green_credentials (accessed February 2022).

Boracay, Boranotokay : Environmental Rehabilitation

 

Hello and welcome back to the 2nd part of Boracay, Boranotokay! This blog post will continue the exploration of Boracay’s  tourism impacts on environmental pollution through the focus on the government measures implemented, and more specifically, the island closure in 2018.

With the aggravation of the island’s environmental condition, President Rodrigo Duterte enacted a 6 month islandwide closure in 2018 in efforts to rehabilitate the environment of Boracay (Reyes et al., 2018). During this period, no tourists were allowed to enter the island and an extensive clean up was initiated by the government. Furthermore, more regulations were for enforced to mitigate the reoccurrence of such devastating environmental pollution on the island. One major source of the marine pollution that occurred in Boracay was the lack of sewage infrastructure which resulted in a direct dumping of sewage water into the ocean. To tackle this, Boracay establishments that have over 50 rooms have been mandated by the government to have their own sewage treatment plans before the re-opening, as well as an accreditation of a tourism facility before they can operate (Cable News Network, 2018). In a study done about the detection of algal bloom in the coastal waters of Boracay, it was subsequently found that there was a reported decrease in the amount of coliform bacteria after rehabilitation (Visitacion, 2019) (figure 1.). This suggests an improvement in the water quality after the rehabilitation process, illustrating the effectiveness of the island closure.

 

Figure 1.

 

However, the island closure has significant socioeconomic repercussions on the islanders living in Boracay. For one, the locals who count on tourism to generate their income suffer greatly economically. The abrupt announcement of closure by President Duterte shocked many businesses on the island, leaving these locals to have to scramble to find alternative sources of income. The shock was so significant that a lawsuit was filed against the closure to the Philippines Supreme Court, expressing that the island closure was more like a “death sentence” to the locals (Haynes, 2018). Furthermore, in the midst of restoring the forests and wetlands of the area, many locals have been evicted from their houses due to the ambivalent legality of their tenure (Board, n.d.). Though the island closure provides time and opportunity for the environment in Boracay to heal, the implicated socioeconomic effects on the locals have been severe.

To end off this post, I would like to once again encourage you as a reader to reflect on the substantial effects of such a remedy to environmental pollution: Do you think that it is possible for us to regularly close off an entire tourist destination to rehabilitate the environment and what are the ramifications for those decisions?

 

References

Board, J. (n.d.) ‘Closing Boracay: How the Philippines shut down paradise’. Available at: https://infographics.channelnewsasia.com/interactive/closing-boracay-the-environment-10181082/index.html (accessed February 2022).

Cable News Network (2018) ‘Boracay reopens after six-month extensive clean-up’, CNN. Available at: https://www.cnnphilippines.com/news/2018/10/26/boracay-reopens-after-cleanup-denr-aklan.html (accessed February 2022).

Haynes, S. (2018) ‘Boracay Island Closure Leaves Residents Feeling the Pinch’, Time. Available at: https://time.com/5262455/boracay-island-philippines-tourists-closure-duterte/ (accessed February 2022).

Reyes, C.M., Albert, J.R.G., Quimba, F.M.A., Ortiz, M.K.P. & Asis, R.D. (2018) The Boracay closure: Socioeconomic consequences and resilience management, Working Paper 2018–37. PIDS Discussion Paper Series.

Visitacion, M.R., Alnin, C.A., Ferrer, M.R. & Suñiga, L. (2019) ‘Detection of Algal Bloom in the Coastal Waters of Boracay, Philippines Using Normalized Difference Vegetation Index (NDVI) and Floating Algae Index (GAI)’, The International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, XLII-4/W19.

 

 

 

Boracay, Boranotokay

 

What You Should Know About Visiting Boracay In The New Normal (UPDATED 2021) - KKday Blog

 

Travelling around the world is a dream for many, including myself! On the list of places that I would love to travel to, Boracay, Philippines stands near the top of the list because of their insanely beautiful beaches.

Boracay is a small tropical island located in the Aklan province in the Western Visayas Region, most renowned by tourists for its ‘powdery’ white beaches, attracting over 600,000 tourists in 2008 alone (Ong et al., 2011). Due to its popularity amongst travellers and the income that is subsequently generated through these tourists, the Philippine government has designated Boracay as the country’s number one beach (Ong et al., 2011).

However, with the amount of attention garnered over the past few years, Boracay has come into serious trouble with the problem of pollution. In 2017, 2 million tourists paid a visit to Boracay, of which the island generated 90 to 115 tonnes of trash every day, causing the island’s dumping sites to be strained due to the high influx of waste generated every day (Board, n.d.). As such, these trash that are undisposed off properly create issues of health and sanitation to the locals in the area, where bacteria and pests thrive off the presence of undisposed garbage, breeding disease vectors (Ayilara, 2020).

Furthermore, wastewater has been pumped directly into the sea due to the lack of wastewater management. In 2018, an abundance of green algae was detected along the coastal waters of the island, indicating a high nutrient discharge, leading to concerns about the water quality by scientists (Visitacion et al., 2019). The polluted waters not only disrupt the marine and aquatic ecosystem due to the process of eutrophication (Wilkinson, 2017), but it threatens the health of those who take a swim in the waters along the coast as they get exposed to the toxins of harmful algal blooms (National Institute of Environmental Health Sciences, 2021).

As such, due to the devastating environmental pollution caused by the tourists, the island closed its borders in 2018 for environmental rehabilitation, of which we will be visiting in the next post. To end off this post and as a lead up to the next, I would like to leave a question for you as a reader to reflect upon: have you ever thought about how much waste you produce when you travel overseas and the implications that it has on the local environment and community? Definitely, it is something scary yet necessary to think about.

 

 

References

Ayilara, M., Olanrewaju, O., Babalola, O. & Odeyemi, O. (2020) ‘Waste Management through Composting: Challenges and Potentials’, Sustainability, 12, 4456.

Board, J. (n.d.) ‘Closing Boracay: How the Philippines shut down paradise’. Available at: https://infographics.channelnewsasia.com/interactive/closing-boracay-the-environment-10181082/index.html (accessed February 2022).

National Institute of Environmental Health Sciences (2021) ‘Algal Blooms’, National Institute of Environmental Health Sciences. Available at: https://www.niehs.nih.gov/health/topics/agents/algal-blooms/index.cfm (accessed February 2022).

Ong, L.T.J., Storey, D. & Minnery, J. (2011) ‘Beyond the Beach: Balancing Environmental and Socio-cultural Sustainability in Boracay, the Philippines’, Tourism Geographies, 13, 549–569.

Visitacion, M.R., Alnin, C.A., Ferrer, M.R. & Suñiga, L. (2019) ‘Detection of Algal Bloom in the Coastal Waters of Boracay, Philippines Using Normalized Difference Vegetation Index (NDVI) and Floating Algae Index (GAI)’, The International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, XLII-4/W19.

Wilkinson, G.M. (2017) ‘Eutrophication of Freshwater and Coastal Ecosystems’, in Abraham, M. A. (ed.) Encyclopedia of Sustainable Technologies, Oxford: Elsevier, 145–152.

Trash at the Peak: Solutions & Responses

In the previous post, Mount Everest was introduced as an area of tourist-induced environmental pollution. To further delve into the subject matter, this blog post will bring in the solutions and responses of the Nepalese government, evaluating their effectiveness in curbing the negative environmental impacts of climbing Mount Everest.

With reference to the previous post, the government has stepped up by implementing initiatives to combat the problem of waste and contaminants being discarded through banning single-use plastics in the region and asking for a 4000 dollar deposit, which would be returned if the climbers brought their waste back down with them (Napper et al., 2020). With these regulations implemented, the production and consumption of single-use plastics is curbed almost entirely, where the carbon emissions released to manufacture these single-use plastics are essentially curbed as well. Statistically, the plastic production to carbon dioxide release ratio is 1:5 , which essentially means that for every ton of single-use plastic produced, 5 tons of carbon emissions is released into the atmosphere (Ramsden, 2020). Furthermore, trekkers are deterred from leaving their waste on the mountain as well due to the financial costs of doing so. This illustrates a significant step towards sustainability in carbon emissions and discarded waste in Nepal by the Nepalese government.

However, one problem that was brought up in the previous post was the issue of microplastics. Though the above-mentioned regulations have tackled a bulk of the environmental pollution issues on Mount Everest, it does not overcome the problem of microplastics. Firstly, as microplastics particles are smaller than 5mm in size (Wu et al., 2016), they are too minute to be picked up and discarded by hand. Additionally, the microplastics discarded on the mountain also derive from the synthetic fibres of the equipment of the trekkers (Napper et al., 2020). Realistically, it is not feasible for the Nepalese government to place a ban on the climbers equipment nor would it be realistic for all trekkers to change their gear to made out of non-synthetic fibres due to the economical costs of these changes.

Ultimately, it does seem that the Nepalese government are ensuring environmental sustainability for the future of Mount Everest and the local community residing there. Nonetheless, it is evident that there are certain elements of pollutants that are not as easily dealt with, of which the onus should be handed to the direct consumers themselves, the climbers to make that change.

References

Napper, I.E., Davies, B.F.R., Clifford, H., Elvin, S., Koldewey, H.J., Mayewski, P.A., Miner, K.R., Potocki, M., Elmore, A.C., Gajurel, A.P. & Thompson, R.C. (2020) ‘Reaching New Heights in Plastic Pollution—Preliminary Findings of Microplastics on Mount Everest’, One Earth, 3, 621–630.

Ramsden, K. (2020) ‘Single-use Plastic & Alternatives’, PSCI. Available at: https://psci.princeton.edu/tips/2020/3/30/single-use-plastic-amp-alternatives (accessed February 2022).

Wu, W.-M., Yang, J. & Criddle, C.S. (2016) ‘Microplastics pollution and reduction strategies’, Frontiers of Environmental Science & Engineering, 11, 6.

Trash at the Peak: Pollution on Mount Everest

For the next two weeks, this blog will explore popular and niche tourist destinations and how the influx of tourists in these areas have cataclysmic effects on the environment and the people living in it.

Every year, more and more trekkers climb Mount Everest, which results in an accumulating amount of trash and pollution in the area. Due to the time-intensive nature of the climb, trekkers spend weeks on the mountain, generating an estimate of around 8 kilograms of waste, of which majority is discarded on the mountain (National Geographic, 2019). The waste found on the mountain range from empty oxygen canisters to food containers to even human faeces. Furthermore, with global warming causing the snow and ice to melt, garbage that has been buried under the snow would resurface, polluting and posing a serious health risk to the local community who live in the Everest watershed. When the watershed becomes contaminated, the local community’s health is threatened as faeces-contaminated water is known to have caused the spread of waterborne diseases such as Cholera (Oguttu et al., 2017).

Additionally, In 2020, researchers from the University of Plymouth collected eight 900 millilitre samples of stream water and eleven 300 millilitre samples of snow from different points of Mount Everest, discovering the presence of microplastics on all of the snow samples and three of the stream water samples (Charles, 2020). These microplastics are thought to have come from synthetic fibres of which are used to make the clothes and the equipment that the Mount Everest trekkers use (Napper et al., 2020). These microplastics found in stream water samples and snow samples would eventually be directly consumed by the local community, causing dire health issues.

Upon evaluation, there is a sort of environmental injustice played out here, where trekkers who climb Mount Everest are the ones polluting the area, while the local, less represented community living in the Everest Watershed have to bear the consequences. In this regard, we will explore what he Nepalese government have done to combat this environmental injustice and create a discourse to analyse whether the initiatives implemented are sufficient in protecting the health and safety of their people while protecting the environment of the area?

References

Charles, K. (2020) ‘Microplastic pollution discovered near the top of Mount Everest’, New Scientist. Available at: https://www.newscientist.com/article/2260499-microplastic-pollution-discovered-near-the-top-of-mount-everest/ (accessed February 2022).

Napper, I.E., Davies, B.F.R., Clifford, H., Elvin, S., Koldewey, H.J., Mayewski, P.A., Miner, K.R., Potocki, M., Elmore, A.C., Gajurel, A.P. & Thompson, R.C. (2020) ‘Reaching New Heights in Plastic Pollution—Preliminary Findings of Microplastics on Mount Everest’, One Earth, 3, 621–630.

National Geographic (2019) ‘Trash and Overcrowding at the Top of the World’, National Geographic.

Oguttu, D.W., Okullo, A., Bwire, G., Nsubuga, P. & Ario, A.R. (2017) ‘Cholera outbreak caused by drinking lake water contaminated with human faeces in Kaiso Village, Hoima District, Western Uganda, October 2015’, Infectious Diseases of Poverty, 6, 146.

 

Nian Culture: A Review of Initiatives Implemented To Reduce Air Pollution

With reference to the journal article on “The impacts of Chinese Nian culture on air pollution” by Ye et al., (2016), this blog post will analyse and dissect the initiatives to reduce the air pollution released during the Chinese New Year period due to cultural practices and beliefs.

There must first be an understanding of exactly how Nian Culture exacerbates the issue of air pollution in Chinese society. According to Chinese mythology, setting off fireworks was a way in which the people could create loud sounds and fire simultaneously to scare off Nian, the evil monster that emerged on New Year’s Eve (Ye et al., 2014). Furthermore, paper money is also burnt more frequently during the Chinese New Year period, with the belief that the ancestors of the individual would be encouraged to protect them. It was found that during the Chinese New Year period, people burn more than 100,000 tons of paper money, creating a tremendous amount of smog, ash and fire (Tang, 2013).

The journal article by Ye et al., (2016) has suggested several initiatives implemented to curb the emission of air pollution. One example would be that the Hangzhou Municipal government issued a notification to encourage celebrating Chinese New Year with a reduction of fireworks, with many internet users supporting this initiative. Some environmentalists have taken a step further, trampling balloons as an alternative towards lighting fireworks. Though reducing air pollution, the alternative usage of balloons maybe create unintended waste when these balloons are not disposed of properly. When not properly disposed, the remnants of the balloons may end up in the ocean, disrupting the lives of marine and aquatic animals as these animals may get injured or killed as a result of balloon entanglement. In a 2016 article from the journal of Marine Policy, it was found that balloon debris ranks just behind fishing lines and plastic bags, as the greatest risk to marine wildlife (Wilcox et al., 2016). Thus, environmental alternatives to reduce air pollution may have unintended consequences on other aspects of environmental pollution, illustrating the complexity in solving environmental problems while managing societal beliefs.

The problem with this Nian Culture derives from the long-standing beliefs of the Chinese community, whereby these practices and beliefs have been integrated deeply into Chinese society, making it extremely difficult to change (Ye et al., 2016). Definitely, the initiatives are a step in the right direction, but the complexity of the long-standing cultural beliefs and practices in society will continue to remain a giant roadblock towards environmental sustainability.

 

References

Tang, Z. (2013) ‘The Environmental Cost of Chinese New Year’, Caijing Review.

Wilcox, C., Mallos, N.J., Leonard, G.H., Rodriguez, A. & Hardesty, B.D. (2016) ‘Using expert elicitation to estimate the impacts of plastic pollution on marine wildlife’, Marine Policy, 65, 107–114.

Ye, C., Chen, R. & Chen, M. (2016) ‘The impacts of Chinese Nian culture on air pollution’, Journal of Cleaner Production, 112, 1740–1745.

Ye, C., Chen, R. & Young, C. (2014) ‘Nian: when Chinese mythology affects air pollution’, The Lancet, 383, 2125.

 

 

Chinese New Year Fireworks!

During this week, in line with the week of Chinese New Year (CNY) festivities, I will be focusing on how various celebrations and holidays have damaging and pollutive effects on the environment. For this post specifically, I will be focusing on the environmental impacts of Chinese New Year fireworks.

Integral to CNY celebrations, Chinese communities light firecrackers with the believe that the bright lights and sound would drive away evil spirits. For example, the new year festivities in China have led to sharp spikes in air pollution, where the fireworks have released extraordinarily high levels or airborne particulate matter (Lai and Brimblecombe, 2020). The fireworks ban recently introduced ahead of the Beijing Winter Olympics by the Beijing government illustrated the marked difference in airborne particles with and without the usage of firecrackers. The average concentrations of these small airborne particles stood at a whopping 289 micrograms per cubic metre during CNY eve before the ban as compared to a mere 5 micrograms per cubic metre after the ban was implemented (CNA, 2022). This illustrates the high intensity of airborne particles released during every CNY celebration while simultaneously also showing how a ban on fireworks is effective in reducing air pollution.

Besides releasing small airborne particles, fireworks have also been found by a study to be a source of ozone, generated through spontaneous bursts in the absence of sunlight and nitrogen oxide (Atrri et al., 2001). Further experiments by the same study has found a linear regression between the total amount of inflammable material present in sparklers and the cumulative O3 formed. This is because the sparklers require a varying combination of metal salts such as sulphur, aluminium nitrate and manganese, which when burnt, produce radiative energy that dissociate the atmospheric molecular oxygen into atomic oxygen, allowing O3 to form (Attri et al., 2001). The tropospheric ozone formed becomes hazardous to people’s health, causing damage in lung tissues, eye irritation and chest congestion (UCAR, 2014).

Despite the negative environmental impacts and negative human health impacts, I believe that fireworks are not an environmental threat that can be eliminated easily due to its significance embedded in CNY traditions and history, to which science and asian cultural beliefs clash. Despite this, the firework ban in Beijing demonstrates a greater awareness by larger institutions of the environmental repercussions of fireworks, bringing us a step closer towards a greener and cleaner earth.

 

References

Attri, A.K., Kumar, U. & Jain, V.K. (2001) ‘Formation of ozone by fireworks’, Nature, 411, 1015–1015.

CNA (2022) ‘Fireworks ban pays off as Beijing records best air quality for Chinese New Year’s eve’, CNA. Available at: https://www.channelnewsasia.com/asia/fireworks-ban-pays-beijing-records-best-air-quality-chinese-new-years-eve-2472656 (accessed February 2022).

Lai, Y. & Brimblecombe, P. (2020) ‘Changes in air pollution and attitude to fireworks in Beijing’, Atmospheric Environment, 231, 117549.

UCAR (2014) ‘Ozone in the Troposphere | Center for Science Education’. Available at: https://scied.ucar.edu/learning-zone/air-quality/ozone-troposphere (accessed February 2022).