thesis impact on environment

Scholars' Bank

Environmental studies theses and dissertations, permanent uri for this collection.

Impacts of Pollution Control, Ecosystem Conservation, and Infrastructure on the Agriculture-Land-Environment Nexus

A major challenge of achieving sustainable development is to balance two critical targets with finite resources: to secure food security for a growing population with rising consumption demands, and to prevent further pollution into the environment and losses in ecosystem services. More importantly, the targets of food production and environment protection are not only related to socio-economic and technological development, but also tangled together both ecologically and economically, in particular regarding competition for land – the necessary natural resource for achieving both targets. In view of this, a comprehensive understanding about how to achieve sustainable development requires integrated analyses of the nexus of agricultural production, land use and environmental protection (the “agriculture-land-environment nexus”), interactions between these components,  and their responses to socio-economic development and policies. 

This dissertation consists of three essays focusing on the impacts of environmental protection polices and infrastructure on the agriculture-land-environment nexus. The first essay analyzes how pollution reduction influences ecosystem services, with both a theoretical model and also empirical analysis with city-level data from China. Existing literature from the environmental and ecological fields reports that pollution reduction contributes to ecosystem services, but the ecosystem effects via economic channels remain under-addressed. We find when integrated together with an economic system, the reduction of pollution causes losses in the area of natural land that supports ecosystem services, which is further supported by empirical evidence. This finding emphasizes the importance of taking ecosystem effects into account on the design, implementation and evaluation of pollution control policies.

The second essay researches the impact of a large-scale forestry and grassland conservation policy in China, the grain-to-green project (GTGP), on cropland supply and crop production. In this essay, we first develop a theoretical model of the relationships between cropland supply, land value (with market access as proxy) and GTGP, and then empirically test these relationships using gridded data from China. We find GTGP not only directly reduces cropland area, but also restricts the elasticity of cropland supply in response to market access. Furthermore, we apply the GTGP’s impacts on cropland supply elasticity on a grid-solving computable model, in order to both validate the model and elasticity estimates via hindcasting and evaluate the GTGP’s impact on agricultural production via simulation. In the computable model where all grids are connected with crop markets, we find two effects of GTGP on agriculture: the direct effect that restricts cropland use and crop production in regions where it is implemented, and the indirect effect that increases crop production on regions not restricted or less restricted by GTGP. Essay 2 contributes to the literature by not only estimating the pattern of gridded cropland supply in China, but also reveals the indirect effect of GTGP on agriculture, which has seldom been researched. 

The third essay researches the impact of transportation infrastructure on Brazilian agriculture, land use, and greenhouse gas (GHG) emissions. Combining a geographic information system (GIS) based analysis and computable model simulation, we find the expansion of infrastructure mainly contributes to the transportation cost reduction in inland Brazil and causes local cropland expansion and increased GHG emissions from land conversion. However, the shifting of crop production towards inland Brazil reduces the demand for cropland in southeastern and southern Brazil, which offsets the impact on cropland expansion and GHG emissions at the national level. Findings in Essay 3 indicate the importance of capturing both spatial heterogeneity and spatial spillover effects of infrastructure expansion when evaluating agricultural and environmental impacts. 

Innovations at the Nexus of Food, Energy, and Water Systems (INFEWS: U.S.-China): A multi-scale integrated modeling approach to managing the transition to sustainability

Directorate for Engineering

CNH2-L: Uncovering Metacoupled Socio-Environmental Systems

Directorate for Biological Sciences

AccelNet:GLASSNET: Networking Global to Local Analyses to Inform Sustainable Investments in Land and Water Resources

Office of the Director

Projeto Rural Sustentável – Cerrado

Degree type.

• Doctor of Philosophy
• Agricultural Economics

Campus location

• West Lafayette

Advisor/Supervisor/Committee Chair

Additional committee member 2, additional committee member 3, additional committee member 4, usage metrics.

• Agricultural spatial analysis and modelling
• Environmental management
• Agricultural economics
• Environment and resource economics

CUNY Academic Works

• < Previous

Home > CUNY Graduate Center > Dissertations, Theses, and Capstone Projects > 1906

Dissertations, Theses, and Capstone Projects

Overpopulation and the impact on the environment.

Doris Baus , The Graduate Center, City University of New York Follow

Date of Degree

Document type, degree name.

Liberal Studies

Sophia Perdikaris

Subject Categories

Agricultural and Resource Economics | Demography, Population, and Ecology | Economics | Education Policy | Environmental Policy | Environmental Studies | Family, Life Course, and Society | Growth and Development | Health Economics | Health Policy | International and Area Studies | International Relations | Place and Environment | Politics and Social Change | Social and Behavioral Sciences | Urban Studies | Urban Studies and Planning

overpopulation, environmental impact, malthus, population growth, environmental issues, causes of overpopulation

In this research paper, the main focus is on the issue of overpopulation and its impact on the environment. The growing size of the global population is not an issue that appeared within the past couple of decades, but its origins come from the prehistoric time and extend to the very present day. Throughout the history, acknowledged scientists introduced the concept of “overpopulation” and predicted the future consequences if the world follows the same behavioral pattern. According to predictions, scientists invented the birth control pill and set population control through eugenics. Despite that, population continued to increase and fight with constant diseases. Migration was another component that encouraged population rise, which imposes severe threats to the environment. Urbanization destroys natural habitats and reinforces carbon dioxide emissions, which cause climate change and global warming. Species are becoming extinct and humanity is at threat that it set up for itself. Food scarcity and shortage of water as well as lack of job opportunities and inadequate education are the results of global inequality. Uneven distribution of natural resources, financial means, and individual rights give rise to poverty and define the global culture as greedy, despite the aid of international organizations and agencies. Solutions to overpopulation lie in the efforts of national institutions to implement policies that will correspond to the guidelines given by international institutions that work for the best of the global community. Within this global network, individuals act in their best interest, leaving the rest in extreme poverty and shortage. The inequality supports issues that contribute to overpopulation and leads to a humanity’s extinction.

Recommended Citation

Baus, Doris, "Overpopulation and the Impact on the Environment" (2017). CUNY Academic Works. https://academicworks.cuny.edu/gc_etds/1906

Included in

Agricultural and Resource Economics Commons , Demography, Population, and Ecology Commons , Education Policy Commons , Environmental Policy Commons , Environmental Studies Commons , Family, Life Course, and Society Commons , Growth and Development Commons , Health Economics Commons , Health Policy Commons , International and Area Studies Commons , International Relations Commons , Place and Environment Commons , Politics and Social Change Commons , Urban Studies Commons , Urban Studies and Planning Commons

• Colleges, Schools, Centers
• Disciplines

Advanced Search

• Notify me via email or RSS

Author Corner

• Submission Policies
• Submit Work
• CUNY Graduate Center

Home | About | FAQ | My Account | Accessibility Statement

Privacy Copyright

Advertisement

Impact of tourism development upon environmental sustainability: a suggested framework for sustainable ecotourism

• Research Article
• Published: 19 August 2022
• Volume 30 , pages 5917–5930, ( 2023 )

Cite this article

• Qadar Bakhsh Baloch 1 ,
• Syed Naseeb Shah 1 ,
• Nadeem Iqbal 2 ,
• Muhammad Sheeraz 3 ,
• Muhammad Asadullah 4 ,
• Sourath Mahar 5 &
• Asia Umar Khan 6  

68k Accesses

7 Altmetric

Explore all metrics

The empirical research investigated the relationship between tourism development and environmental suitability to propose a framework for sustainable ecotourism. The framework suggested a balance between business and environmental interests in maintaining an ecological system with the moderating help of government support and policy interventions. The study population encompasses tourism stakeholders, including tourists, representatives from local communities, members of civil administration, hoteliers, and tour operators serving the areas. A total of 650 questionnaires were distributed to respondents, along with a brief description of key study variables to develop a better understanding. After verifying the instrument’s reliability and validity, data analysis was conducted via hierarchical regression. The study findings revealed that a substantial number of people perceive socio-economic benefits, including employment and business openings, infrastructure development from tourism development, and growth. However, the state of the natural and environmental capital was found to be gradually degrading. Alongside the social environment, social vulnerability is reported due to the overutilization of land, intrusion from external cultures, and pollution in air and water due to traffic congestion, accumulation of solid waste, sewage, and carbon emissions. The study suggested a model framework for the development of sustained ecotourism, including supportive government policy interventions to ensure effective conservation of environmental and natural resources without compromising the economic viability and social well-beings of the locals. Furthermore, the variables and the constructs researched can be replicated to other destinations to seek valuable inputs for sustainable destination management elsewhere.

Similar content being viewed by others

Balancing tourism and conservation: analysing the sustainability of tourism in the city of Naples through citizen perspectives

Sustainable Tourism Indicators in Cities

Ecotourism as a Core of Sustainability in Tourism

Explore related subjects.

• Environmental Chemistry

Avoid common mistakes on your manuscript.

Introduction

Tourism is a vibrant force that stimulates travel to explore nature, adventures, wonders, and societies, discover cultures, meet people, interact with values, and experience new traditions and events. Tourism development attracts tourists to a particular destination to develop and sustain a tourism industry. Moreover, environmental sustainability is the future-based conscious effort aimed at conserving socio-cultural heritage and preserving natural resources to protect environmental ecosystems through supporting people’s health and economic well-being. Environment sustainability can be reflected in clean and green natural landscaping, thriving biodiversity, virgin sea beaches, long stretches of desert steppes, socio-cultural values, and archeological heritage that epitomize tourists’ degree of motivation and willingness of the local community to welcome the visitors. In this context, tourism growth and environmental sustainability are considered interdependent constructs; therefore, the increase in tourism development and tourists’ arrivals directly affects the quality of sustained and green tourism (Azam et al. 2018 ; Hassan et al.  2020 ; Sun et al. 2021 ).

According to the World Tourism Organization (UNWTO), tourism is one of the fastest-growing industries, contributing more than 10% to the global GDP (UNWTO 2017; Mikayilov et al. 2019 ). Twenty-five million international tourists in 1950 grew to 166 million in 1970, reaching 1.442 billion in 2018 and projected to be 1.8 billion by 2030. Mobilizing such a substantial human tourist’s mass is most likely to trickle environmental pollution along with its positive effects on employment, wealth creation, and the economy. The local pollution at tourist destinations may include air emissions, noise, solid waste, littering, sewage, oil and chemicals, architectural/visual pollution, heating, car use, and many more. In addition, an uncontrolled, overcrowded, and ill-planned tourist population has substantial adverse effects on the quality of the environment. It results in the over-consumption of natural resources, degradation of service quality, and an exponential increase in wastage and pollution. Furthermore, tourism arrivals beyond capacity bring problems rather than a blessing, such as leaving behind soil erosion, attrition of natural resources, accumulation of waste and air pollution, and endangering biodiversity, decomposition of socio-cultural habitats, and virginity of land and sea (Kostić et al. 2016 ; Shaheen et al. 2019 ; Andlib and Salcedo-Castro  2021 ).

Tourism growth and environmental pollution have been witnessed around the globe in different regions. The ASEAN countries referred to as heaven for air pollution, climate change, and global warming are experiencing economic tourism and pollution (Azam et al. 2018 ; Guzel and Okumus 2020 ). In China, more than fifty-eight major Chinese tourism destinations are inviting immediate policy measures to mitigate air pollution and improve environmental sustainability (Zhang et al. 2020 ). Similarly, Singapore, being a top-visited country, is facing negative ecological footprints and calling for a trade-off between tourism development and environmental sustainability (Khoi et al. 2021 ). The prior studies established that international tourism and the tourism-led growth surge tourists’ arrival, energy consumption, carbon dioxide (CO 2 ) emissions, and air pollution resultantly cause climate change (Aslan et al. 2021 ). South Asian countries, more specifically Sri Lanka and Pakistan, are on the verge of tourism growth and environmental pollution compared to other countries (Chishti et al. 2020 ; Tiwari et al. 2021 ).

Pakistan is acknowledged in the tourism world because of its magnificent mountains with the densest concentration of high peaks in the world, scenic beauty of Neelum Valley, Murree, Chitral, and swat Valleys’, Kaghan, Naran, Hunza, Gilgit Baltistan (Baloch 2007 ), sacred shrines of Sikhism, archeological sites of the Gandhara and Indus Valley civilizations such as Mohenjo-Daro, Taxila including pre-Islamic Kalasha community (Baloch and Rehman 2015 ). In addition, Pakistan’s hospitable and multicultural society offers rich traditions, customs, and festivals for the tourists to explore, commemorate, cherish, and enjoy. Pakistan’s geographical and socio-cultural environment represents its resource and an opportunity (Baloch and Rehman 2015 ); therefore, Pakistan is looking to capitalize on it as a promising source of the foreign reserve to compensate for its mounting trade deficit (Baloch et al. 2020 ).

Tourism expansion has been established as a very deleterious ecological cost vis-à-vis the socio-economic benefits it passes to the host communities (Pulido-Fernández et al. 2019 ; Simo-Kengne 2022 ). In this context, the research is motivated to investigate the relationships between Pakistan’s tourism development activities and environmental sustainability. Drawing from the arguments of Pulido-Fernández et al. ( 2019 ) and Simo-Kengne ( 2022 ), it is feared that Pakistan’s ongoing determination to tourism development is likely to cause environmental degradation in two ways. Firstly, the tourism infrastructure developmental process would consume natural resources in the form of air and water pollution, loss of nature, and biodiversity. Secondly, the proliferation of tourism-related energy-consuming activities harms the environment by adding CO 2  emissions (Andlib and Saceldo-Castro 2021 ; Chien et al. 2021a ). Therefore, to tape this tourism-rich potential without compromising the sustainability of the natural and socio-cultural environment in the area, there is a dire need to develop Pakistan’s tourism areas into environment-friendly destinations.

Against the backdrop of a widening level of trade deficit, Pakistan’s rich tourism potential is being perceived as an immediate alternative for earning revenue to compensate for the current account gap. However, the developing large-scale tourism industry is considered a threat to deforestation, and air and water pollution, endangering biodiversity trading on resilient ecological credentials. The research study attempts to find an all-inclusive and comprehensive answer to the socio-ecological environmental concerns of tourism development and growth. Therefore, the research investigates the relationship between tourism development and its environmental sustainability to suggest a model framework for the development and growth of Sustainable Ecotourism in Pakistan along with its most visited destinations.

Literature review

• Tourism development and growth

Tourism is considered a force of sound as it benefits travelers and communities in urban and suburban areas. Tourism development is the process of forming and sustaining a business for a particular or mix of segments of tourists’ as per their motivation in a particular area or at a specific destination. Primarily, tourism development refers to the all-encompassing process of planning, pursuing, and executing strategies to establish, develop, promote, and encourage tourism in a particular area or destination (Mandić et al. 2018 ; Ratnasari et al. 2020 ). A tourism destination may serve as a single motivation for a group of tourists or a mix of purposes, i.e., natural tourism, socio-cultural or religious tourism, adventure or business tourism, or a combination of two or more. Andlib and Salcedo-Castro ( 2021 ), drawing from an analysis approach, contended that tourism destinations in Pakistan offer a mix of promising and negative consequences concerning their socio-economic and environmental impressions on the host community. The promising socio-economic impacts for the local community are perceived in the form of employment and business opportunities, improved standard of living, and infrastructural development in the area. The adverse environmental outcomes include overcrowding, traffic congestion, air and noise pollution, environmental degradation, and encroachment of landscaping for the local community and the tourists. An extensive review of the literature exercise suggests the following benefits that the local community and the tourists accrue from the tour are as follows:

Generate revenue and monetary support for people and the community through local arts and culture commercialization.

Improve local resource infrastructure and quality of life, including employment generation and access to improved civic facilities.

Help to create awareness and understanding of different ethnic cultures, social values, and traditions, connecting them and preserving cultures.

Rehabilitate and conserve socio-cultural and historical heritage, including archeological and natural sites.

Establishment of natural parks, protracted areas, and scenic beauty spots.

Conservation of nature, biodiversity, and endangered species with control over animal poaching.

Improved water and air quality through afforestation, littering control, land and soil conservation, and recycling of used water and waste.

Tourism and hospitality business incorporates various business activities such as travel and transportation through the air or other modes of travel, lodging, messing, restaurants, and tourism destinations (Szpilko 2017 ; Bakhriddinovna and Qizi 2020 ). A tourist’s tourism experience is aimed at leisure, experiencing adventure, learning the culture or history of a particular area or ethnic entity, traveling for business or health, education, or religious purposes. The chain of activities adds value to the Tourism experience. Every activity contributes toward economic stimulation, job creation, revenue generation, and tourism development encompassing infrastructure for all activities involved in the tourism process. Tourism growth expresses the number of arrivals and the time of their stay/trips over a period of time. Tourism growth is measured through the interplay between tourists’ arrivals, tourism receipts, and travel time duration (Song et al. 2010 ; Arifin et al. 2019 ). The following factors drive the degree and level of tourism development and growth:

Environmental factors include scenic beauty, green spaces, snowy mountains, towering peaks, good climate and weather, the interconnectivity of destination, quality of infrastructure, etc.

Socio-economic factors: the distinctiveness of community, uniqueness of culture and social values, hospitality and adaptability, accessibility, accommodation, facilities and amenities, cost-effectiveness, price index, and enabling business environment.

Historical, cultural, and religious factors include historical and cultural heritage, religious sites, and cultural values and experiences.

The tourism development process and its different dynamics revolve around the nature of tourism planned for a particular destination or area, which can be specified as ecotourism, sustainable tourism, green tourism or regenerative tourism, etc. Ecotourism is “responsible travel to natural areas that conserves the environment, sustains the well-being of the local people, and involves interpretation and education” (Cheia, 2013 ; TIES, 2015). According to the World Conservation Union (IUCN), ecotourism involves “ Environmentally responsible travel to natural areas, to enjoy and appreciate nature (and accompanying cultural features, both past, and present) that promote conservation, have a low visitor impact and provide for beneficially active socio-economic involvement of local peoples ”. Moreover, Blangy and Wood ( 1993 ) defined it as “ responsible travel to natural areas that conserves the environment and sustains the well-being of local people ” (p. 32). The concept of ecotourism is grounded upon a well-defined set of principles including “environmental conservation and education, cultural preservation and experience, and economic benefits” (Cobbinah 2015 ; De Grosbois and Fennell 2021 ).

Ecotourism minimizes tourism’s impact on the tourism resources of a specific destination, including lessening physical, social, interactive, and psychosomatic impacts. Ecotourism is also about demonstrating a positive and responsible attitude from the tourists and hosts toward protecting and preserving all components of the environmental ecosystem. Ecotourism reflects a purpose-oriented mindset, responsible for creating and delivering value for the destination with a high degree of kindliness for local environmental, political, or social issues. Ecotourism generally differs from mass tourism because of its following features (Liang et al. 2018 ; Ding and Cao 2019 ; Confente and Scarpi 2021 ):

Conscientious behavior focuses on the low impact on the environment.

Sensitivity and warmth for local cultures, values, and biodiversity.

Supporting the sustenance of efforts for the conservation of local resources.

Sharing and delivering tourism benefits to the local communities.

Local participation as a tourism stakeholder in the decision-making process.

Educating the tourist and locals about the sensitivity and care of the environment because tourism without proper arrangement can endanger the ecosystems and indigenous cultures and lead to significant ecological degradation.

Sustainability aims to recognize all impacts of tourism, minimize the adverse impacts, and maximize the encouraging ones. Sustainable tourism involves sustainable practices to maintain viable support for the ecology of the tourism environment in and around the destination. Sustainable tourism is natural resource-based tourism that resembles ecotourism and focuses on creating travel openings with marginal impact and encouraging learning about nature having a low impact, conservation, and valuable consideration for the local community’s well-being (Fennell 2001 & 2020 ; Butowski 2021 ). On the other hand, ecotourism inspires tourists to learn and care about the environment and effectively participate in the conservation of nature and cultural activities. Therefore, ecotourism is inclusive of sustainable tourism, whereas the focus of sustainable tourism includes the following responsibilities:

Caring, protecting, and conserving the environment, natural capital, biodiversity, and wildlife.

Delivering socio-economic welfare for the people living in and around tourists' destinations.

Identifying, rehabilitating, conserving, and promoting cultural and historical heritage for visitors learning experiences.

Bringing tourists and local groups together for shared benefits.

Creating wide-ranging and reachable opportunities for tourists.

Environment and sustainability of ecosystem

The term “environment” is all-inclusive of all the natural, organic living, inorganic, and non-natural things. The environment also denotes the interface among all breathing species with the natural resources and other constituents of the environment. Humans’ activities are mainly responsible for environmental damage as people and nations have contemplated modifying the environment to suit their expediencies. Deforestation, overpopulation, exhaustion of natural capital, and accumulation of solid waste and sewage are the major human activities that result in polluted air and water, acid rain, amplified carbon dioxide levels, depletion of the ozone, climate change, global warming, extermination of species, etc. A clean, green, and hygienic fit environment has clean air, clean water, clean energy, and moderate temperature for the healthy living of humans, animals, and biodiversity as nature is destined for them by their creatures. Maintaining and sustaining a clean environment is indispensable for human and biodiversity existence, fostering growth and development for conducting business and creating wealth. The environment can be sustained through conservation, preservation, and appropriate management to provide clean air, water, and food safe from toxic contamination, waste, and sewage disposal, saving endangered species and land conservation.

The globalization process, known for building socio-economic partnerships across countries, is also charged with encouraging environmental degradation through the over-consumption of natural resources and energy consumption, deforestation, land erosion, and weakening (Adebayo and Kirikkaleli 2021 ; Sun et al. 2021 ). Chien et al. ( 2021b ), while studying the causality of environmental degradation in Pakistan, empirically confirmed the existence of a significant connection between CO 2  emissions and GDP growth, renewable energy, technological innovation, and globalization. However, Chien et al. ( 2021a ) suggested using solar energy as a source of economic intervention to control CO 2  emissions and improve environmental quality in China. The danger of air pollution is hard to escape as microscopic air pollutants pierce through the human respiratory and cardiovascular system, injuring the lungs, heart, and brain. Ill-planned and uncontrolled human activities negatively affect ecosystems, causing climate change, ocean acidification, melting glaciers, habitation loss, eutrophication, air pollution, contaminants, and extinction of endangered species ( Albrich et al. 2020 ) .

Humans have a more significant effect on their physical environment in numerous ways, such as pollution, contamination, overpopulation, deforestation, burning fossil fuels and driving to soil erosion, polluting air and water quality, climate change, etc. UNO Agenda for 2030 “Sustainable Development and its Sustainable Development Goals” (SDGs) mirrors the common premise that a healthy environment and human health are interlaced as integral to the satisfaction of fundamental human rights, i.e., right to life, well-being, food, water and sanitation, quality of life and biodiversity to ensure healthy lives and promote well-being for all at all ages (SDG3)—which includes air quality that is dependent upon terrestrial ecosystems (SDG15), oceans (SDG14), cities (SDG11), water, cleanliness, and hygiene (SDG6) (Swain 2018 ; Opoku 2019 ; Scharlemann et al. 2020 ). The UNEP stated that 58% of diarrhea cases in developing economies is due to the non-provision of clean water and inadequate sanitation facilities resulting in 3.5 million deaths globally (Desai 2016 ; Ekins and Gupta 2019 ).

Climate change overwhelmingly alters ecosystems’ ability to moderate life-threatening happenings, such as maintaining water quality, regulating water flows, unbalancing the temporal weather and maintaining glaciers, displacing or extinction biodiversity, wildfire, and drought (Zhu et al. 2019 ; Marengo et al. 2021 ). Research studies advocate that exposure to natural environments is correlated with mental health, and proximity to green space is associated with lowering stress and minimizing depression and anxiety (Noordzij et al. 2020 ; Slater et al. 2020 ; Callaghan et al. 2021 ). Furthermore, the Ecosystem is affected by pollution, over-exploitation of natural resources, climate change, invasive and displacing species, etc. Hence, providing clean air and water, hygienic places, and green spaces enriches the quality of life: condensed mortality, healthier value-added productivity, and is vital to maintaining mental health. On the other hand, climate change aggravates environment-related health hazards through adverse deviations to terrestrial ecology, oceans, biodiversity, and access to fresh and clean water.

Tourism development denotes all activities linked with creating and processing facilities providing services for the tourists on and around a destination. Infrastructure development is vital for developing a tourism destination to advance tourists’ living conditions and preserve natural and cultural heritage by constructing new tourist facilities, the destinations administrative and supporting echelons, including community living, etc. Development for tourism infrastructure and land use often burdens natural capital through over-consumption, leading to soil erosion, augmented pollution, loss of natural habitats, and endangered species. Development of tourism infrastructure and construction work has profound implications on environmental degradation, reduction in green spaces, deforestation, solid waste and sewage, overutilization of air and water, emission of CO 2 and other gases contributing to air and water pollution, climate change, loss and displacement of biodiversity, and the degradation of ecosystems. These negative consequences of tourism development result in many problems for the tourists and the indigenous people in the foreseeable future (Azam et al. 2018 ; Hoang et al. 2020 ).

A report published by UNEP titled “Infrastructure for climate action” has suggested governments introduce sustainable infrastructure as the prevailing one is responsible for causing 79% of all greenhouse gas emissions in struggling climate change, alleviation, and adaptation efforts. Sustainable infrastructure signifies that structures’ planning, construction, and functioning do not weaken the social, economic, and ecological systems (UNEP 2021 ; Krampe 2021 ). Sustainable infrastructure is the only solution that ensures societies, nature, and the environment flourish together. Therefore, Sustainable Ecotourism supports adapting pro-environment and nature-based climate change strategies that help resilient biodiversity and ecosystem to impact climate change. The proposed strategy is to focus on the conservation and restoration of ecosystems to combat climate hazards, fluctuating rainfalls, soil erosion, temperature variations, floods, and extreme wind storms (Niedziółka 2014 ; Setini 2021 )

Pakistan’s tourism infrastructure suffered a colossal amount of damage during the earthquake of October 8, 2005, which left widespread demolition and destruction to its human, economic assets, and infrastructure networks, especially in Kashmir and Khyber Pakhtunkhwa's tourism areas. The tourism-related infrastructure, including hotels, destination facilities of social service delivery and commerce, water channels, and communications networks, were either drained or virtually destroyed. The destruction in the aftermath of the earthquake was further added by the war against terror in tourism-hit areas, resulting in the redundancy of tourists and tourism facilities for a long time (Akbar et al. 2017 ; Zakaria and Ahmed 2019 ). The tourism revival activities during the post-earth quack, post-terrorism scenario, and COVID-19 period called for various entrepreneurial activities, including the construction of infrastructure, hotels, road networks, community living, etc. Development and reconstruction of the livelihood and hospitality infrastructure through entrepreneurship were undertaken intensively through a public-private partnership from national and international findings (Qamar and Baloch 2017 ; Sadiq 2021 ; Dogar et al. 2021 ).

The revival and reinvigoration of infrastructure in tourism areas were backed up by extensive deforestation, use of local green land, rebuilding of the road network, displacement of biodiversity, and overtaxing the consumption of water and other natural resources. The deforestation, extensive use of green land, and over-consumption of water and other natural resources have depleted the tourism value of the area on the one hand and degraded the environment on the other. However, it was the focused rehabilitation activities of earthquake and Pakistan’s Government’s socio-environment conservation strategy of the Billion Trees plantation program in the province, including dominating tourism areas. The afforestation and loss of green tops are being reclaimed through these efforts, and the tourism environment is soon expected to regenerate (Qamar and Baloch 2017 ; Rauf et al. 2019 ; Siddiqui and Siddiqui 2019 ).

Government support and policy interventions

Tourism generates wide-ranging benefits for the economy, community, and people. Tourism contributes to the economy through revenue generation and shares responsibility with the Government to alleviate poverty alleviation, create opportunities for job placements, protect environments, and conserve natural ecosystems and biodiversity. It is assumed that if the tourism industry is left to its own, it will most likely prefer its business interests over environments or biodiversity. Governments, custodians of the life and well-being of their subjects, are directly responsible for providing a clean environment, nature, and Ecosystem. Therefore, national and local governments are responsible for preparing and implementing tourism development plans and enforcing values and standards for tourism development in conformity with the prerequisites of environmental sustainability. Through institutional governance, governments help tourism development by providing financial and budgetary support, regulatory framework, land, physical resources, infrastructure, etc. Provision and facilitation for Sustainability of Ecotourism and conservation of environment and biodiversity are dependent upon Government-supported interventions as follows:

The regulatory framework for setting up tourism-related entrepreneurship and quality standards can support ecotourism and prevent environmental degradation on any account.

Provision of budgetary support for ecosystem conservation and regeneration of bio-diversity-related projects.

Plan, rehabilitate if needed, promote conservation and protection of socio-cultural, historic, antique, and natural endowments in coordination with other public and private agencies, and deal with the defaulters, if any.

Promoting and undertaking afforestation alongside land conservation and discouraging deforestation, soil erosion, accumulation of solid waste, littering, and any direct or indirect loss or threat to biodiversity.

Setting restrictions for over-tourism beyond capacity and quality standards for transportation, restaurants, hotels, food and drinking water, etc.

Placing enforcement mechanism necessary to ensure application of the regulatory framework and quality standards applicable along with all activities inclusive to the Ecotourism value chain.

Theoretical support and hypothesis development

According to the social disruption theory, rapidly expanding societies usually experience a period of widespread crisis and a loss of their conventional routines and attitudes. The crisis impacts people whose mental health, worldviews, behavioral patterns, and social networks may all be impacted (Çalişkan and Özer 2021 ). According to the social disruption theory, fast community change brought on by population growth will result in a variety of social issues that are signs of a generally disorganized community (Smith et al. 2001 ). Because some types of tourism communities experience rapid expansion accompanied by intensive development and rapid social change over a relatively short period of time, they seem to be great settings for studying various postulations of the social disruption theory.

Place change and social disruption theory are closely connected. According to this assumption, when a community undergoes fast expansion, it tends to experience a generalized crisis that might culminate in several social issues as changes spread throughout the community and among individuals (Rasoolimanesh et al. 2019 ). Place change can result from fundamental community restructuring due to economic development, new class divides, and migration of both long-term and temporary people (Nelson 2001 ). Social unrest, though, is not enduring. Instead, it is transitory; societies gradually adjust to these changes (Deery et al.  2012 ).

The standard of living may initially deteriorate, but due to the adaptability of people and communities, they will gradually reinvigorate and strengthen themselves accordingly. Furthermore, the social disruption proposition reinforces one of the challenges in analyzing the effects of tourism, particularly in emerging nations, since it is sometimes difficult to distinguish between the effects of tourism and the overall ongoing development (Park and Stokowski 2009 ) (Fig. 1 ).

Tourism development and growth significantly affect natural environment resources.

Tourism development and growth significantly affect environmental pollution.

Tourism development and growth significantly affect the physical ecosystem of the environment.

Tourism development and growth significantly affect the socio-cultural environment.

Tourism development and growth significantly affect the economic environment of people and the community.

Government policy and support significantly moderate the relationship between tourism development and growth and the environmental factors.

Conceptual framework

Methodology

The study aimed to investigate the association of tourism development and its impact on environmental factors. Therefore, a survey method was employed to collect data by including all the relevant people in the locality. The study is based on stakeholders’ opinions from Pakistan’s most visited tourist areas, including Murree, Swat, Chitral, Naran, Kaghan, Neelum Valley, Malam Jabba, Ayubia, and Nathia Gali. A total of 650 stakeholders were contacted from the above-mentioned tourist destinations through survey. The distribution of the sample is mentioned in Table 1 .

Using quantitative techniques, hierarchical linear regression analysis was employed to investigate the possible relationships between tourism growth and various dimensions of environmental sustainability. The results below reveal that tourism development translates into environmental deterioration, and the relationship between tourism and environmental sustainability is bidirectional.

Tourism growth and development were measured through a five-item scale. The environment was measured through 16 items combined scale with sub-dimensions; depletion of Natural Resources=3 items, Polluting Environment=3 items, Physical Effects on Ecosystem=4 items, Socio-Cultural Degradation=3 items, and Economic Environment=3-items. Similarly, our moderating variable, Government Interventions and Support, was measured using a 5-item scale. Table 2 below presents the details of the instruments.

Analysis and results

Data were analyzed using SPSS Version 26. It includes correlation, linear regression, and stepwise hierarchal regression analysis.

Table 3 above shows that our Tourism Growth and Development has significant and positive relationship with Polluting Environment ( r = 0.20**), Physical Effects on Ecosystem ( r = 0.19**), Depletion of Natural Resource ( r = 0.24**), Socio-Cultural Degradation ( r = 0.18**). However, Tourism Growth and Development has positive relationship with Economic Environment ( r = 0.29**) and Government Interventions and Support ( r = 0.13**).

Results of linear regression analysis at Table 4 above depict that tourism growth and development predicts 4.1% variance in Depletion of Natural Resources ( β = 0.20, p <0.01), 3.9% variance in pollution ( β = 0.19, p <0.01), 6% variance in Physical Effects on Ecosystem ( β = 0.24, p <0.01), 3.6% variance in Socio-Cultural Degradation ( β = 0.18, p <0.01), and 8.8% variance in Economic Environment ( β = 0.29, p <0.01).

The study analyzes the applied two-step hierarchal regression. In the first step, Tourism Growth and Government Interventions were treated as independent variables, and their significant impact was measured. In the second step, the interaction term Tourism and Growth× Government Interventions was added, and its impact was measured. The results suggest that Government Interventions and Support moderate the relationship between Tourism Growth and the Environmental variables (Table 5 ).

The study has reported unique findings regarding tourism and its environmental impacts. We found that tourism growth and development generate economic activity on the one hand. However, it has specific adverse environmental and socio-cultural outcomes on the other hand as well. Our study revealed that tourism growth and development predict a 4.1% variance in Depletion of Natural Resources ( β = 0.202*, p <0.01). This suggests that due to the expansion of tourism in the country, natural resources are continuously depleted to meet the needs of tourists. Studies also supported our findings and suggested that revival and reinvigoration of infrastructure in tourism areas were backed up by extensive deforestation, use of local green land, rebuilding of the road network, displacement of biodiversity, and overtaxing the consumption of water and other natural resources (Qamar and Baloch 2017 ; Sadiq 2021 ; Dogar et al. 2021 ). The prior studies are consistent with our hypothesis that “tourism development and growth significantly affect natural environment resources.”

We further found that tourism growth and development predict a 3.9% variance in pollution ( β = 0.198*, p <0.01), suggesting that tourism expansion may pollute the natural environment. Furthermore, recent national statistics depict that major human activities at local tourism destinations such as Kalam, Sawat, Muree, and Northern Areas have accumulated solid waste and sewage, resulting in polluted air and water. Further, research also suggests that the overflow of tourists to tourist destinations may adversely affect the environment due to human activities (Noordzij et al. 2020 ; Slater et al. 2020 ; Andlib and Salcedo-Castro  2021 ; Callaghan et al. 2021 ). Thus, it is safe to argue that the growth of tourism has a particularly detrimental effect on the environment. These findings also support our hypothesis, “Tourism development and growth significantly contribute to environmental pollution.”

The results reported that tourism growth and development predict a 6% variance in Physical Effects on the Ecosystem ( β = 0.245*, p <0.01). Studies have reported that deforestation and alteration in species’ natural environment for tourism facilities construction may adversely affect environmental health (Kuvan, 2010 ; Azam et al. 2018 ; Hoang et al. 2020 ; Andlib and Salcedo-Castro  2021 ). During post-terrorism and post-Covid-19 times in Pakistan, millions of local tourists moved to popular tourist destinations that required new infrastructure to accommodate these tourists. Consequently, colossal deforestation and other detrimental human activities have negatively affected ecosystem. These findings also support our hypothesis that tourism development and growth significantly affect the physical ecosystem of the environment.

The study reported a total of 3.6% variance in socio-cultural degradation ( β = 0.189*, p <0.01) due to tourism growth and development. These findings suggest that tourism’s growth and development may lead the inhabitants to imitate the foreign tourists regarding their living standards, which may endanger their traditional culture. Thus, our hypothesis that “tourism development and growth significantly affect the socio-cultural environment” is confirmed.

Further, it was found that tourism growth and development predict an 8.8% variance in the economic environment ( β = 0.297*, p <0.01). It is established from the literature that tourism growth and development generate economic activity in the country. Development projects such as the construction of infrastructure, hotels, and road networks generate economic activity to facilitate international and indigenous tourists, positively affecting the community’s living standard (Baloch et al. 2020 ). Thus, our hypothesis, “tourism development and growth significantly affect economic environment of people and community,” is confirmed.

Due to tourism growth and development, our study reported a 1.8% variance in Government Support and Interventions ( β = .133*, p <0.01). However, more recently, the Government of Pakistan has devised specific interventions that may help curb the adverse impacts of detrimental environmental factors. For example, developmental schemes such as the Billion Trees Plantation drive and Road-Infrastructure Network Development under the China-Pakistan Economic Corridor initiative may prove moderators to curb the negative impacts of tourism growth on the environment (Qamar and Baloch 2017 ; Rauf et al. 2019 ; Siddiqui and Siddiqui 2019 ). Therefore, the hypothesis, Government policy and support, significantly moderates the relationship between tourism development and growth with the environment is confirmed based on these findings.

Suggested model for ecotourism framework

Through its detailed review of existing literature, prevailing tourism policies, and empirical inputs from the stakeholders’ perspectives, the study has identified a wide range of obstacles limiting the development and growth of ecotourism in Pakistan. The study suggests National Tourism Management authorities carefully invest in ecotourism destination’s planning and development in coordination with the environment development agency. The suggested model for ecotourism framework is initially meant for the tourism destinations specifically designated for ecotourism. However, selected points can also be extended to the quality management parameters set for the National Parks, Conservation and Protracted Areas, Museums, National or International event sites, etc. The national tourism authorities are to lay particular emphasis in their forthcoming National Tourism Policy on the development and promotion of Sustainable Ecotourism having, with focus on the following key areas:

Identify and classify four to five ecotourism destinations, including ecotourism-centered activities of value chains for priority development, which are administratively possible within budgetary constraints. However, the development plan shall consider the integral benefits of other developmental schemes such as the Billion Trees Plantation drive, Road-Infrastructure Network Development under the China-Pakistan Economic Corridor initiative, International Union for Conservation of Nature (ICUN) programs in the area.

While staying within the alignment of UN Millennium Development Goals (MDG) calling for ‘environmental sustainability’ and the development vision of each designated destination, the Tourists Management System shall take into cognizance of issues like managing capacity of the place, quality parameters for the conservation of the environment, and allowable activities thereof.

Identify degenerated destinations of religious, socio-cultural, or historical significance for their rehabilitation under the Regenerated tourism program.

Tourism Destinations that have been over-consumed and exhausted (e.g., Murree, Galiaat, Naran, Malam Jabba) because of over-tourism shall be planned for their reclamation through regenerated tourism. However, to facilitate the success of the regeneration of their tourism potential following is to be catered for:

To deflect the tourist pressure upon these destinations, the potential tourists from nearby cities and metropolitan areas be provided with nearby alternative destinations for leisure tourism as stay-tourism sites.

To prevent the environment from air pollution, the traffic load on the destination be curtailed through an effective traffic management strategy, provision of off-destination parking for combustion engine vehicles, and encouraging electric driven or hybrid vehicles for nearby parking.

Provision of clean drinking water through public infiltration plants, public toilets, solid waste carriers, and recycling of sewage and used water is recommended in the most visited areas of the destination.

Signposting at appropriate places, giving social messages encouraging to maintain cleanliness, avoid littering, ensure nature conservation, and humility toward biodiversity.

Develop all-inclusive, comprehensive execution plans to expedite the investments for the sustainable ecotourism, encouraging public–private cooperation, community involvement, and infrastructure mapping guaranteeing environmental conservation and safeguards.

Develop and place on the ground an all-inclusive program of capacity building for sustainable ecotourism, regenerative and green tourism services.

Develop and launch Pakistan tourism profile and Sustaining Ecotourism obligatory framework “to promote tourism on the one hand and nurture conscious ecological behavior among the potential tourists of the area”.

In order to fetch local ownership for the ecotourism center developments, all efforts shall be made to share the socio-economic benefits integral to the development scheme with the local population for community development.

As part of the destination management planning, identify complementary value chains and livelihood activities that could be developed as part of the overall ecotourism destination package.

Governments at all levels and the tourism Development and Promotion Agencies Network in Pakistan shall join hands to chalk out and, with a strict enforcement mechanism, a “Regulatory Framework for Ecotourism Friendly Destination” to sustain the efforts and policies undertaken in this regard on the one hand and generate responsible behavior from the tourism stakeholders on the other. Some of the suggestive points could be:

Setting new quality standards facilitating the promotion of ecotourism and environmental sustainability through acts of various bodies operating in the Ecotourism value chain, such as:

Revision of Private hotels Management Act (1976) and Tourists Operators Act (1976) alongside introduction and promulgation of a new “Tourism Destination Management Act” incorporating new quality standards as of today.

Promulgating laws to make all new construction/development projects responsible from any agency in the area, incorporating quality standards needed for environmental sustainability, and promoting ecotourism.

Set measures for the preservation of the local biodiversity and preservation of endangered species, including seeking support from internationally active environment conservation agencies, declaring local hunting illegal, introducing licensing programs for hunting of certain selected animals/ birds on the payment of a handsome amount to be used for the welfare of the local community.

Create awareness programs against deforestation, land conservation, and biodiversity, and maintain cleanliness, inculcating a culture of respecting and enjoying nature instead of spoiling it.

Conclusion, implications, and limitations of the study

The study premise was based on the contention that sustenance of ecotourism focuses on the economic viability of the business interests alongside the conservation and preservation of natural ecosystems, including ethical fairness to the socio-cultural environment of the host community. Ecotourism is a phenomenon that contributes to environmental sustainability through well-planned and careful destination management capable of balancing conflicting interests of business growth and environmental sustainability. Tourism-environment paradox suggests that the sustainability and survival of both are dependent upon the flourishing mode of each other. Quality of environment and sustainability of bio-ecosystem stimulates tourists’ arrivals and over-tourism beyond capacity with irresponsible behavior from tourists negatively influencing the environment and harming the ecosystem of nature. Ecotourism is not inevitably sustainable unless it is economically sustainable and environmentally maintainable besides being socio-culturally acceptable. Socio-culturally intolerable ecotourism means the activity which does not benefit locals and their socio-cultural values. Hence, the study concludes that ecotourism has to positively interplay between economy, environment, and culture without compromising one over others. The pursuit of sustainable ecotourism is not an end in meeting the little comforts of the business interests but rather a means to end the sustainability issues created due to ill-conceived tourism development and unmanageable growth.

Practical implications

Drawing from the findings and conclusions of the research, the study extends the following practical implications for effectively managing the process of tourism development and environmental sustainability in line with the dictates of the philosophy behind ecotourism:

Paradoxically tourism necessitates ecological capitals as primary ingredients for the creation of tourism experiences on the one hand. However, it is also contingent upon the conservation and preservation of ecological integrity on the other. The study suggests that unbalancing this “resource paradox” results in the harshness and tenacity of adversarial climate change, natural calamities, environmental pollution, and endangered biodiversity.

The research findings and the suggested framework for ecotourism imply that sustainable ecotourism principles-based planning is mandatory for destination management to assure effective trade-off between the business interests’ sustainability of the environmental ecosystem.

Tourism development and growth shall be steered through ecotourism principles as its sustainable model offers enduring social, environmental and economic, ecological integrity, and social and cultural benefits for the local community. Therefore, ecotourism is a recipe for preventing environmental degradation and guarantees sustainability of ecosystems nature and its biodiversity. Hence, ecotourism shall stand central priority focus for strategic management to nurture quality experiences from sustainable tourism.

To revive back the sustainability of the environment, in the areas where over-tourism has degraded the environment, schemes for regenerated tourism shall be immediately launched to mitigate the negative footprints on the sustainability of destinations, including reinforcing protracted conservation sites, biodiversity, and recouping endangered species, afforestation drives, recycling of water and solid waste, refurnishing of landscaping, preservation, and rehabilitation of cultural heritage and refurbishing of depleted infrastructure accordingly. Furthermore, to regenerate and sustain the tourism infrastructure of the destinations experiencing over-tourism, capacity building measures like capacity, recycling of water and solid waste, preventive measures to control air and water pollution, traffic control management, and spread of entertainment facilities shall be the focus of the regeneration plans.

The study implies that government authorities and policymakers have a special role in placing their moderating intervention in terms of policy guidelines, regulatory framework, and budgetary support, provision of inter-organizational synergy in planning and implementation of ecotourism strategies, protection of environmental resource base and conservation of natural and biological ecosystem, sustenance of socio-cultural value of local community over and above their economic and social well-being/quality life for the long run.

The study also implies that public and private policymakers lay down threshold criteria for responsible travel and tourism standards for destination management and its related supply chain. The laid criterion would facilitate management in nurturing “responsible behavior” to plan, protect, conserve, preserve, and sustain natural and cultural resources and responsible socio-economic development without compromising the sustainability of the environment and long-term well-being of the hoist community. The deep-seated adherence to social responsibility protocols by the tourism supply chain network can significantly increase the capacity of tourism destinations and improve the conscious awareness of green consumers along the tourism supply chain. Furthermore, the consciously responsible behavior among stakeholders and legislatures can strike a needed balance between the business interests and environments in favor of sustainability of socio-cultural, economic, and natural capital.

The study elucidates that responsible behavior necessitates purpose-built eco-friendly infrastructure and policy parameters to support the sustainability of environments across destinations. The strategic planning aligned with the sustainability-focused objectives dictates the need for artistic, innovative, and talented people and quality intuitions in harnessing quality tourism services and responsible tourism behavior. Furthermore, the study encourages community involvement in the developmental process, enactment of structural policies, preservation of socio-cultural heritage, and conservation of natural biodiversity as it would foster emotional bondage between the people of the host community and the tourism undertakings. Therefore, community and value chain managers shall collaborate to maximize the perceived benefits of responsible tourism while developing cultural exchanges and planning opportunities for leisure and tourism.

Regulatory measures help offset negative impacts; for instance, controls on the number of tourist activities and movement of visitors within protected areas can limit impacts on the ecosystem and help maintain the integrity and vitality of the site. Limits should be established after an in-depth analysis of the maximum sustainable visitor capacity. Furthermore, the variables and the constructs researched can be replicated to other destinations to seek valuable inputs for sustainable destination management elsewhere.

Study limitation

Besides the functional, practical applications, the study has some limitations. Besides having integral disadvantages of cross-sectional research, the respondents selected for the study were visitors on peak days with the highest tourist arrivals, thereby having experiences of a higher degree of environmental pollution and natural disorder. Furthermore, the research is limited to stakeholders’ perspectives instead of any scientifically generated data or mathematical or econometric model.

Author information

Authors and affiliations.

Abasyn University, Peshawar, Pakistan

Qadar Bakhsh Baloch & Syed Naseeb Shah

Air University School of Management, Air University, Islamabad, Pakistan

Nadeem Iqbal

Department of Commerce, Bahauddin Zakariya University, Multan, Pakistan

Muhammad Sheeraz

IBA, Gomal University, Dera Ismail Khan, Pakistan

Muhammad Asadullah

University of Sialkot, Sialkot, Pakistan

Sourath Mahar

Islamia College University Peshawar, Peshawar, Pakistan

Asia Umar Khan

You can also search for this author in PubMed   Google Scholar

Contributions

QBB: conceptualization, methodology, writing—original draft. SNS: data curation and supervision. NI: visualization, editing, proofreading. MS: review and editing. MA: review and editing. SM: editing, data curation. AUK: review and editing.

Corresponding author

Correspondence to Nadeem Iqbal .

Ethics declarations

Ethics approval and consent to participate.

The authors have no relevant financial or non-financial interests to disclose. We also declare that we do not have human participants, data, or tissue.

Consent for publication

We do not have any person’s data in any form.

Competing interests

The authors declare no competing interests.

Additional information

Responsible Editor: Arshian Sharif

Publisher's note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Rights and permissions

Springer Nature or its licensor holds exclusive rights to this article under a publishing agreement with the author(s) or other rightsholder(s); author self-archiving of the accepted manuscript version of this article is solely governed by the terms of such publishing agreement and applicable law.

Reprints and permissions

About this article

Baloch, Q.B., Shah, S.N., Iqbal, N. et al. Impact of tourism development upon environmental sustainability: a suggested framework for sustainable ecotourism. Environ Sci Pollut Res 30 , 5917–5930 (2023). https://doi.org/10.1007/s11356-022-22496-w

Download citation

Received : 14 December 2021

Accepted : 08 August 2022

Published : 19 August 2022

Issue Date : January 2023

DOI : https://doi.org/10.1007/s11356-022-22496-w

Share this article

Anyone you share the following link with will be able to read this content:

Sorry, a shareable link is not currently available for this article.

Provided by the Springer Nature SharedIt content-sharing initiative

• Environmental sustainability and degradation
• Natural environment
• Ecosystem and biodiversity
• Ecotourism framework
• Find a journal
• Publish with us
• Track your research

Home > Environmental Studies > Student Theses 2001-2013

Student Theses 2001-2013

Theses/dissertations from 2017 2017.

The Disappearing Wetland Act: Climate Change, Development, and Protection , Jessica P. Doughty

Theses/Dissertations from 2013 2013

The Centrality of Ecological Design: Achieving Sustainability in an Era of Free-Market Capitalist Framework , Eddy Andrade

A Vicious CERCLA, Or The Twilight of the Superfund , Donald Borenstein

Saving the World’s Remaining Tigers: Panthera’s Work and the Role of Non-Profits in Wildlife Conservation , John Byrne

New York City’s Water Challenges: History, Politics, and Design , Jessica Crowley

Giving Back to the Community: Addressing the Environmental Literacy Gap Through Socially and Environmentally Responsible Business Practices , David Garcia

Wasting Plates: Addressing Food Waste in the United States , Sarah Geuss

Too Pig to Fail: Considering Regulatory Solutions to the Environmental Damages Caused by Industrial Hog Farms in North Carolina , Samir Hafez

Sandy and the City: The Need for Coastal Policy Reform , Jonathan Hilburg

Drilling for Arctic Oil: Is it Worth the Risk? , Emily Kain

The Pedestrianization of New York City: An Environmental History and Critique of Urban Motorization and A Look at New York City’s New Era of Planning , Anna Kobara

Hurricane Sandy: Using Environmental History, Economics, Politics and Urban Planning to Prepare For the Next One , Julia Maguire

Our Failing Food System: Productivity Versus Sustainability , Alyson Murphy

Exploring the Drivers of CSR and Creating a Sustainable Corporate Institution: Environmental Education, Politics, and Business Practices , Eric Osuna

Composting Food Waste: A Method That Can Improve Soil Quality and Reduce Greenhouse Gas Emissions , Gentiana Quni

Assessment of Impact of Socioeconomic Factors on Conservation Awareness in the Tarangire-Manyara Ecosystem , Karianne Rivera

The Sustainable Future of the Metropolis: Greening New York City Building By Building , Lizbeth Sanchez

Trash Talk: Solid Waste Disposal in New York City , Alexander Williams

Hurricane Sandy: A Chance to Identify Vulnerabilities, Learn from the Past, and Increase Future Resiliency , Julianne Yee

Theses/Dissertations from 2012 2012

Going Green at New York-Presbyterian: Hospitals As Sustainable Businesses , Samantha Allegro

A Stronger Role For the United States President in Environmental Policy , Elizabeth Anderson

Simulating Climate Risk Into Markets and Policies: A New Approach to Financial Analysis and Policy Formation , Miguel Bantigue

Environmental Education Reform: Using Experiential Learning to Influence Environmental Policy-Making By Fostering a Sense of Environmental Citizenship and Eco-Literacy , Nicol Belletiere

Internship Report: Earthjustice & the Fracking Battle in New York's Marcellus Shale , John Byrne

Coal: How We Achieved Our Dependency and Its True Cost , Kelly Caggiano

Recycling Furniture: The Ecological, Economic and Social Benefits , Michele Calabrese

Internship Report UNEP: The Effects of Climate Change in Arctic Zones , Diana Cartaya-Acosta

Environmental Racism in South Africa: A Sustainable Green Solution , Danielle Darmofal

The Bronx, Beavers and Birthrights: The Case For Urban Wildlife , Richard Day

The Economics of Biodiversity , Paige Doyle

Environmental Communications: Case Study of New York City's Double Crested Cormorant , Marisa Galdi

Not a Walk In the Park: Environmental Justice in New York City , Lindsey Grier

The Economic and Environmental Justice Implications of Hydraulic Fracturing in 21st Century North America , Katie Medved

The Bottling Craze: Exposing the Environmental Effects of Bottled Vs. Tap Water , Michele Paccagnini

How the United States Will Find a Sustainable Future Through Increased Nuclear Productivity , Ian Pruitt

Group For the East End: The Role of Childhood Environmental Education in Improving Learning Behaviors and the Health of Humans and the Environment , Brian Riley

The Role of Modern Zoos in Wildlife Conservation: From the WCS to the Wild , John Scott

Global Climate Change Vs. Global Warming: What Is the Difference "Global Climate Change" and "Global Warming"? , Nadia Seeteram

Lost in Translation: Environmental Communication Issues in Media and Politics , Carolyn Wegemann

Theses/Dissertations from 2011 2011

The Ins and Outs of Corporate Greenwashing , Jennifer Bender

A River Runs Through It: Community Access to the Bronx River in Tremont and Hunts Point , Matthew Bodnar

The Future is Green; Urban Agriculture in the Bronx , Patty Gouris

All in Our Backyard: Exploring how Environmental Discrimination Affects Health and Social Conditions in the South Bronx , Mireille Martineau

Theses/Dissertations from 2010 2010

The Bronx River Alliance: A Model Community Action Organization And an Internship in Development , John Hinck

Enrique Reef: Degradation and Protective Measures , Dana Mitchell

The Human Population Growth and its Ecological Consequences on Kenya and Tanzania , Lauren Noll

Environmental Consciousness: Human Motivation for Thinking Ecologically , Rob Pigue

Economics of Carbon Regulation: An Exploration to the Nuance of Carbon Regulation , Timothy J. Schwartz

New York Botanical Garden Internship: From Photography to Policy , Christine Willeford

Theses/Dissertations from 2009 2009

Environmental Health and Climate Change: The Case of Lyme Disease , Matthew Abad

Recycling Tendencies of Fordham University's Population , Jeremy Aiss, Vincent Ammirato, Anamarie Beluch, and Christopher Torres

The Business of Sustainability , Andrea Brady

Waste Mismanagement: Fighting Environmental Injustice in Mott Haven and Hunts Point , Elizabeth Friedrich

Environmental Internship & The Fordham Eco-Roof Proposal , Anthony Giovannone

The Putnam Railroad Corridor Restoration Project: A Comprehensive Plan for Paired Ecological Restoration and Greenway Construction , Patrick J. Hopkins Jr.

Land Use Policy and Development on Long Island , Richard Murdocco

From the Bronx into the Wild! My Adventurous Experience at the Bronx Zoo , Lauren Noll

For the Birds! , Robert Patterson

Managing Infestation of the Invasive Viburnum Leaf Beetle (Pyrrhalta viburni) at the New York Botanical Garden , Gregory Russo

Environmental History of Japan , Amy Seagroves

Theses/Dissertations from 2008 2008

A Healthy Environment is a Healthy Body , Matthew Abad

Stormwater Runoff, Combined Sewer Overflow, and Environmental Justice in the Bronx , Natalie Collao

Solving a Crisis: Water Quality & Storm Water Infrastructure in New York City , Kelsey Ripper

The New Social Movement: Environmental Justice in the Bronx , Kelsey Ripper

Environmental Justice and Street Science: A Fusion of Community Knowledge and Environmental Health Justice to Address the Asthma Epidemic in Urban Communities , Natalie Robiou

Urban Wildlife and Leopold’s Land Ethic: “The squirrels on a college campus convey the same lesson as the redwoods. . . .” , Natalie Robiou

Unpasteurized Milk and Soft Cheese Outbreaks: An Overview of Consumer Safety , Taygan Yilmaz

Theses/Dissertations from 2007 2007

The Environmental Justice Movement in the United States , Harrison Delfin

Natural River Restoration in Urban Ecology: The Bronx River , Samuel P. Loor

Theses/Dissertations from 2006 2006

The H5N1 Avian Influenza Virus: Globalization, Climate Change, and Other Anthropogenic Factors in New Emergent Diseases , Quan Luong

The Environmental Effects of War , Philip Swintek

Theses/Dissertations from 2005 2005

Identification of Genetically Modified Organisms in Foodstuffs , Anamarie Beluch

The Moral Dilemma of Genetically Modified Foods (GMOs) , Anamarie Beluch

Theses/Dissertations from 2003 2003

The History of Community Gardens in New York City: The Role of Urban Agriculture and Green Roofs in Addressing Environmental Racism , Rosamarie Ridge

Theses/Dissertations from 2002 2002

Bronx River Restoration: Report and Assessment , Teresa Crimmens

Environmental Audit of the Rose Hill Campus , Nicole Marshall, Maria Nissi, Brian Flaherty, Carl Van Ostrand, and Ian McClelland

Theses/Dissertations from 2001 2001

Bronx River Restoration: Report and Assessment , Nicole Marshall

Advanced Search

• Notify me via email or RSS
• Collections
• Disciplines

Author Corner

Home | About | FAQ | My Account | Accessibility Statement

Privacy Copyright

REVIEW article

Environmental and health impacts of air pollution: a review.

• 1 Delphis S.A., Kifisia, Greece
• 2 Laboratory of Hygiene and Environmental Protection, Faculty of Medicine, Democritus University of Thrace, Alexandroupolis, Greece
• 3 Centre Hospitalier Universitaire Vaudois (CHUV), Service de Médicine Interne, Lausanne, Switzerland
• 4 School of Social and Political Sciences, University of Glasgow, Glasgow, United Kingdom

One of our era's greatest scourges is air pollution, on account not only of its impact on climate change but also its impact on public and individual health due to increasing morbidity and mortality. There are many pollutants that are major factors in disease in humans. Among them, Particulate Matter (PM), particles of variable but very small diameter, penetrate the respiratory system via inhalation, causing respiratory and cardiovascular diseases, reproductive and central nervous system dysfunctions, and cancer. Despite the fact that ozone in the stratosphere plays a protective role against ultraviolet irradiation, it is harmful when in high concentration at ground level, also affecting the respiratory and cardiovascular system. Furthermore, nitrogen oxide, sulfur dioxide, Volatile Organic Compounds (VOCs), dioxins, and polycyclic aromatic hydrocarbons (PAHs) are all considered air pollutants that are harmful to humans. Carbon monoxide can even provoke direct poisoning when breathed in at high levels. Heavy metals such as lead, when absorbed into the human body, can lead to direct poisoning or chronic intoxication, depending on exposure. Diseases occurring from the aforementioned substances include principally respiratory problems such as Chronic Obstructive Pulmonary Disease (COPD), asthma, bronchiolitis, and also lung cancer, cardiovascular events, central nervous system dysfunctions, and cutaneous diseases. Last but not least, climate change resulting from environmental pollution affects the geographical distribution of many infectious diseases, as do natural disasters. The only way to tackle this problem is through public awareness coupled with a multidisciplinary approach by scientific experts; national and international organizations must address the emergence of this threat and propose sustainable solutions.

Approach to the Problem

The interactions between humans and their physical surroundings have been extensively studied, as multiple human activities influence the environment. The environment is a coupling of the biotic (living organisms and microorganisms) and the abiotic (hydrosphere, lithosphere, and atmosphere).

Pollution is defined as the introduction into the environment of substances harmful to humans and other living organisms. Pollutants are harmful solids, liquids, or gases produced in higher than usual concentrations that reduce the quality of our environment.

Human activities have an adverse effect on the environment by polluting the water we drink, the air we breathe, and the soil in which plants grow. Although the industrial revolution was a great success in terms of technology, society, and the provision of multiple services, it also introduced the production of huge quantities of pollutants emitted into the air that are harmful to human health. Without any doubt, the global environmental pollution is considered an international public health issue with multiple facets. Social, economic, and legislative concerns and lifestyle habits are related to this major problem. Clearly, urbanization and industrialization are reaching unprecedented and upsetting proportions worldwide in our era. Anthropogenic air pollution is one of the biggest public health hazards worldwide, given that it accounts for about 9 million deaths per year ( 1 ).

Without a doubt, all of the aforementioned are closely associated with climate change, and in the event of danger, the consequences can be severe for mankind ( 2 ). Climate changes and the effects of global planetary warming seriously affect multiple ecosystems, causing problems such as food safety issues, ice and iceberg melting, animal extinction, and damage to plants ( 3 , 4 ).

Air pollution has various health effects. The health of susceptible and sensitive individuals can be impacted even on low air pollution days. Short-term exposure to air pollutants is closely related to COPD (Chronic Obstructive Pulmonary Disease), cough, shortness of breath, wheezing, asthma, respiratory disease, and high rates of hospitalization (a measurement of morbidity).

The long-term effects associated with air pollution are chronic asthma, pulmonary insufficiency, cardiovascular diseases, and cardiovascular mortality. According to a Swedish cohort study, diabetes seems to be induced after long-term air pollution exposure ( 5 ). Moreover, air pollution seems to have various malign health effects in early human life, such as respiratory, cardiovascular, mental, and perinatal disorders ( 3 ), leading to infant mortality or chronic disease in adult age ( 6 ).

National reports have mentioned the increased risk of morbidity and mortality ( 1 ). These studies were conducted in many places around the world and show a correlation between daily ranges of particulate matter (PM) concentration and daily mortality. Climate shifts and global planetary warming ( 3 ) could aggravate the situation. Besides, increased hospitalization (an index of morbidity) has been registered among the elderly and susceptible individuals for specific reasons. Fine and ultrafine particulate matter seems to be associated with more serious illnesses ( 6 ), as it can invade the deepest parts of the airways and more easily reach the bloodstream.

Air pollution mainly affects those living in large urban areas, where road emissions contribute the most to the degradation of air quality. There is also a danger of industrial accidents, where the spread of a toxic fog can be fatal to the populations of the surrounding areas. The dispersion of pollutants is determined by many parameters, most notably atmospheric stability and wind ( 6 ).

In developing countries ( 7 ), the problem is more serious due to overpopulation and uncontrolled urbanization along with the development of industrialization. This leads to poor air quality, especially in countries with social disparities and a lack of information on sustainable management of the environment. The use of fuels such as wood fuel or solid fuel for domestic needs due to low incomes exposes people to bad-quality, polluted air at home. It is of note that three billion people around the world are using the above sources of energy for their daily heating and cooking needs ( 8 ). In developing countries, the women of the household seem to carry the highest risk for disease development due to their longer duration exposure to the indoor air pollution ( 8 , 9 ). Due to its fast industrial development and overpopulation, China is one of the Asian countries confronting serious air pollution problems ( 10 , 11 ). The lung cancer mortality observed in China is associated with fine particles ( 12 ). As stated already, long-term exposure is associated with deleterious effects on the cardiovascular system ( 3 , 5 ). However, it is interesting to note that cardiovascular diseases have mostly been observed in developed and high-income countries rather than in the developing low-income countries exposed highly to air pollution ( 13 ). Extreme air pollution is recorded in India, where the air quality reaches hazardous levels. New Delhi is one of the more polluted cities in India. Flights in and out of New Delhi International Airport are often canceled due to the reduced visibility associated with air pollution. Pollution is occurring both in urban and rural areas in India due to the fast industrialization, urbanization, and rise in use of motorcycle transportation. Nevertheless, biomass combustion associated with heating and cooking needs and practices is a major source of household air pollution in India and in Nepal ( 14 , 15 ). There is spatial heterogeneity in India, as areas with diverse climatological conditions and population and education levels generate different indoor air qualities, with higher PM 2.5 observed in North Indian states (557–601 μg/m 3 ) compared to the Southern States (183–214 μg/m 3 ) ( 16 , 17 ). The cold climate of the North Indian areas may be the main reason for this, as longer periods at home and more heating are necessary compared to in the tropical climate of Southern India. Household air pollution in India is associated with major health effects, especially in women and young children, who stay indoors for longer periods. Chronic obstructive respiratory disease (CORD) and lung cancer are mostly observed in women, while acute lower respiratory disease is seen in young children under 5 years of age ( 18 ).

Accumulation of air pollution, especially sulfur dioxide and smoke, reaching 1,500 mg/m3, resulted in an increase in the number of deaths (4,000 deaths) in December 1952 in London and in 1963 in New York City (400 deaths) ( 19 ). An association of pollution with mortality was reported on the basis of monitoring of outdoor pollution in six US metropolitan cities ( 20 ). In every case, it seems that mortality was closely related to the levels of fine, inhalable, and sulfate particles more than with the levels of total particulate pollution, aerosol acidity, sulfur dioxide, or nitrogen dioxide ( 20 ).

Furthermore, extremely high levels of pollution are reported in Mexico City and Rio de Janeiro, followed by Milan, Ankara, Melbourne, Tokyo, and Moscow ( 19 ).

Based on the magnitude of the public health impact, it is certain that different kinds of interventions should be taken into account. Success and effectiveness in controlling air pollution, specifically at the local level, have been reported. Adequate technological means are applied considering the source and the nature of the emission as well as its impact on health and the environment. The importance of point sources and non-point sources of air pollution control is reported by Schwela and Köth-Jahr ( 21 ). Without a doubt, a detailed emission inventory must record all sources in a given area. Beyond considering the above sources and their nature, topography and meteorology should also be considered, as stated previously. Assessment of the control policies and methods is often extrapolated from the local to the regional and then to the global scale. Air pollution may be dispersed and transported from one region to another area located far away. Air pollution management means the reduction to acceptable levels or possible elimination of air pollutants whose presence in the air affects our health or the environmental ecosystem. Private and governmental entities and authorities implement actions to ensure the air quality ( 22 ). Air quality standards and guidelines were adopted for the different pollutants by the WHO and EPA as a tool for the management of air quality ( 1 , 23 ). These standards have to be compared to the emissions inventory standards by causal analysis and dispersion modeling in order to reveal the problematic areas ( 24 ). Inventories are generally based on a combination of direct measurements and emissions modeling ( 24 ).

As an example, we state here the control measures at the source through the use of catalytic converters in cars. These are devices that turn the pollutants and toxic gases produced from combustion engines into less-toxic pollutants by catalysis through redox reactions ( 25 ). In Greece, the use of private cars was restricted by tracking their license plates in order to reduce traffic congestion during rush hour ( 25 ).

Concerning industrial emissions, collectors and closed systems can keep the air pollution to the minimal standards imposed by legislation ( 26 ).

Current strategies to improve air quality require an estimation of the economic value of the benefits gained from proposed programs. These proposed programs by public authorities, and directives are issued with guidelines to be respected.

In Europe, air quality limit values AQLVs (Air Quality Limit Values) are issued for setting off planning claims ( 27 ). In the USA, the NAAQS (National Ambient Air Quality Standards) establish the national air quality limit values ( 27 ). While both standards and directives are based on different mechanisms, significant success has been achieved in the reduction of overall emissions and associated health and environmental effects ( 27 ). The European Directive identifies geographical areas of risk exposure as monitoring/assessment zones to record the emission sources and levels of air pollution ( 27 ), whereas the USA establishes global geographical air quality criteria according to the severity of their air quality problem and records all sources of the pollutants and their precursors ( 27 ).

In this vein, funds have been financing, directly or indirectly, projects related to air quality along with the technical infrastructure to maintain good air quality. These plans focus on an inventory of databases from air quality environmental planning awareness campaigns. Moreover, pollution measures of air emissions may be taken for vehicles, machines, and industries in urban areas.

Technological innovation can only be successful if it is able to meet the needs of society. In this sense, technology must reflect the decision-making practices and procedures of those involved in risk assessment and evaluation and act as a facilitator in providing information and assessments to enable decision makers to make the best decisions possible. Summarizing the aforementioned in order to design an effective air quality control strategy, several aspects must be considered: environmental factors and ambient air quality conditions, engineering factors and air pollutant characteristics, and finally, economic operating costs for technological improvement and administrative and legal costs. Considering the economic factor, competitiveness through neoliberal concepts is offering a solution to environmental problems ( 22 ).

The development of environmental governance, along with technological progress, has initiated the deployment of a dialogue. Environmental politics has created objections and points of opposition between different political parties, scientists, media, and governmental and non-governmental organizations ( 22 ). Radical environmental activism actions and movements have been created ( 22 ). The rise of the new information and communication technologies (ICTs) are many times examined as to whether and in which way they have influenced means of communication and social movements such as activism ( 28 ). Since the 1990s, the term “digital activism” has been used increasingly and in many different disciplines ( 29 ). Nowadays, multiple digital technologies can be used to produce a digital activism outcome on environmental issues. More specifically, devices with online capabilities such as computers or mobile phones are being used as a way to pursue change in political and social affairs ( 30 ).

In the present paper, we focus on the sources of environmental pollution in relation to public health and propose some solutions and interventions that may be of interest to environmental legislators and decision makers.

Sources of Exposure

It is known that the majority of environmental pollutants are emitted through large-scale human activities such as the use of industrial machinery, power-producing stations, combustion engines, and cars. Because these activities are performed at such a large scale, they are by far the major contributors to air pollution, with cars estimated to be responsible for approximately 80% of today's pollution ( 31 ). Some other human activities are also influencing our environment to a lesser extent, such as field cultivation techniques, gas stations, fuel tanks heaters, and cleaning procedures ( 32 ), as well as several natural sources, such as volcanic and soil eruptions and forest fires.

The classification of air pollutants is based mainly on the sources producing pollution. Therefore, it is worth mentioning the four main sources, following the classification system: Major sources, Area sources, Mobile sources, and Natural sources.

Major sources include the emission of pollutants from power stations, refineries, and petrochemicals, the chemical and fertilizer industries, metallurgical and other industrial plants, and, finally, municipal incineration.

Indoor area sources include domestic cleaning activities, dry cleaners, printing shops, and petrol stations.

Mobile sources include automobiles, cars, railways, airways, and other types of vehicles.

Finally, natural sources include, as stated previously, physical disasters ( 33 ) such as forest fire, volcanic erosion, dust storms, and agricultural burning.

However, many classification systems have been proposed. Another type of classification is a grouping according to the recipient of the pollution, as follows:

Air pollution is determined as the presence of pollutants in the air in large quantities for long periods. Air pollutants are dispersed particles, hydrocarbons, CO, CO 2 , NO, NO 2 , SO 3 , etc.

Water pollution is organic and inorganic charge and biological charge ( 10 ) at high levels that affect the water quality ( 34 , 35 ).

Soil pollution occurs through the release of chemicals or the disposal of wastes, such as heavy metals, hydrocarbons, and pesticides.

Air pollution can influence the quality of soil and water bodies by polluting precipitation, falling into water and soil environments ( 34 , 36 ). Notably, the chemistry of the soil can be amended due to acid precipitation by affecting plants, cultures, and water quality ( 37 ). Moreover, movement of heavy metals is favored by soil acidity, and metals are so then moving into the watery environment. It is known that heavy metals such as aluminum are noxious to wildlife and fishes. Soil quality seems to be of importance, as soils with low calcium carbonate levels are at increased jeopardy from acid rain. Over and above rain, snow and particulate matter drip into watery ' bodies ( 36 , 38 ).

Lastly, pollution is classified following type of origin:

Radioactive and nuclear pollution , releasing radioactive and nuclear pollutants into water, air, and soil during nuclear explosions and accidents, from nuclear weapons, and through handling or disposal of radioactive sewage.

Radioactive materials can contaminate surface water bodies and, being noxious to the environment, plants, animals, and humans. It is known that several radioactive substances such as radium and uranium concentrate in the bones and can cause cancers ( 38 , 39 ).

Noise pollution is produced by machines, vehicles, traffic noises, and musical installations that are harmful to our hearing.

The World Health Organization introduced the term DALYs. The DALYs for a disease or health condition is defined as the sum of the Years of Life Lost (YLL) due to premature mortality in the population and the Years Lost due to Disability (YLD) for people living with the health condition or its consequences ( 39 ). In Europe, air pollution is the main cause of disability-adjusted life years lost (DALYs), followed by noise pollution. The potential relationships of noise and air pollution with health have been studied ( 40 ). The study found that DALYs related to noise were more important than those related to air pollution, as the effects of environmental noise on cardiovascular disease were independent of air pollution ( 40 ). Environmental noise should be counted as an independent public health risk ( 40 ).

Environmental pollution occurs when changes in the physical, chemical, or biological constituents of the environment (air masses, temperature, climate, etc.) are produced.

Pollutants harm our environment either by increasing levels above normal or by introducing harmful toxic substances. Primary pollutants are directly produced from the above sources, and secondary pollutants are emitted as by-products of the primary ones. Pollutants can be biodegradable or non-biodegradable and of natural origin or anthropogenic, as stated previously. Moreover, their origin can be a unique source (point-source) or dispersed sources.

Pollutants have differences in physical and chemical properties, explaining the discrepancy in their capacity for producing toxic effects. As an example, we state here that aerosol compounds ( 41 – 43 ) have a greater toxicity than gaseous compounds due to their tiny size (solid or liquid) in the atmosphere; they have a greater penetration capacity. Gaseous compounds are eliminated more easily by our respiratory system ( 41 ). These particles are able to damage lungs and can even enter the bloodstream ( 41 ), leading to the premature deaths of millions of people yearly. Moreover, the aerosol acidity ([H+]) seems to considerably enhance the production of secondary organic aerosols (SOA), but this last aspect is not supported by other scientific teams ( 38 ).

Climate and Pollution

Air pollution and climate change are closely related. Climate is the other side of the same coin that reduces the quality of our Earth ( 44 ). Pollutants such as black carbon, methane, tropospheric ozone, and aerosols affect the amount of incoming sunlight. As a result, the temperature of the Earth is increasing, resulting in the melting of ice, icebergs, and glaciers.

In this vein, climatic changes will affect the incidence and prevalence of both residual and imported infections in Europe. Climate and weather affect the duration, timing, and intensity of outbreaks strongly and change the map of infectious diseases in the globe ( 45 ). Mosquito-transmitted parasitic or viral diseases are extremely climate-sensitive, as warming firstly shortens the pathogen incubation period and secondly shifts the geographic map of the vector. Similarly, water-warming following climate changes leads to a high incidence of waterborne infections. Recently, in Europe, eradicated diseases seem to be emerging due to the migration of population, for example, cholera, poliomyelitis, tick-borne encephalitis, and malaria ( 46 ).

The spread of epidemics is associated with natural climate disasters and storms, which seem to occur more frequently nowadays ( 47 ). Malnutrition and disequilibration of the immune system are also associated with the emerging infections affecting public health ( 48 ).

The Chikungunya virus “took the airplane” from the Indian Ocean to Europe, as outbreaks of the disease were registered in Italy ( 49 ) as well as autochthonous cases in France ( 50 ).

An increase in cryptosporidiosis in the United Kingdom and in the Czech Republic seems to have occurred following flooding ( 36 , 51 ).

As stated previously, aerosols compounds are tiny in size and considerably affect the climate. They are able to dissipate sunlight (the albedo phenomenon) by dispersing a quarter of the sun's rays back to space and have cooled the global temperature over the last 30 years ( 52 ).

Air Pollutants

The World Health Organization (WHO) reports on six major air pollutants, namely particle pollution, ground-level ozone, carbon monoxide, sulfur oxides, nitrogen oxides, and lead. Air pollution can have a disastrous effect on all components of the environment, including groundwater, soil, and air. Additionally, it poses a serious threat to living organisms. In this vein, our interest is mainly to focus on these pollutants, as they are related to more extensive and severe problems in human health and environmental impact. Acid rain, global warming, the greenhouse effect, and climate changes have an important ecological impact on air pollution ( 53 ).

Particulate Matter (PM) and Health

Studies have shown a relationship between particulate matter (PM) and adverse health effects, focusing on either short-term (acute) or long-term (chronic) PM exposure.

Particulate matter (PM) is usually formed in the atmosphere as a result of chemical reactions between the different pollutants. The penetration of particles is closely dependent on their size ( 53 ). Particulate Matter (PM) was defined as a term for particles by the United States Environmental Protection Agency ( 54 ). Particulate matter (PM) pollution includes particles with diameters of 10 micrometers (μm) or smaller, called PM 10 , and extremely fine particles with diameters that are generally 2.5 micrometers (μm) and smaller.

Particulate matter contains tiny liquid or solid droplets that can be inhaled and cause serious health effects ( 55 ). Particles <10 μm in diameter (PM 10 ) after inhalation can invade the lungs and even reach the bloodstream. Fine particles, PM 2.5 , pose a greater risk to health ( 6 , 56 ) ( Table 1 ).

Table 1 . Penetrability according to particle size.

Multiple epidemiological studies have been performed on the health effects of PM. A positive relation was shown between both short-term and long-term exposures of PM 2.5 and acute nasopharyngitis ( 56 ). In addition, long-term exposure to PM for years was found to be related to cardiovascular diseases and infant mortality.

Those studies depend on PM 2.5 monitors and are restricted in terms of study area or city area due to a lack of spatially resolved daily PM 2.5 concentration data and, in this way, are not representative of the entire population. Following a recent epidemiological study by the Department of Environmental Health at Harvard School of Public Health (Boston, MA) ( 57 ), it was reported that, as PM 2.5 concentrations vary spatially, an exposure error (Berkson error) seems to be produced, and the relative magnitudes of the short- and long-term effects are not yet completely elucidated. The team developed a PM 2.5 exposure model based on remote sensing data for assessing short- and long-term human exposures ( 57 ). This model permits spatial resolution in short-term effects plus the assessment of long-term effects in the whole population.

Moreover, respiratory diseases and affection of the immune system are registered as long-term chronic effects ( 58 ). It is worth noting that people with asthma, pneumonia, diabetes, and respiratory and cardiovascular diseases are especially susceptible and vulnerable to the effects of PM. PM 2.5 , followed by PM 10 , are strongly associated with diverse respiratory system diseases ( 59 ), as their size permits them to pierce interior spaces ( 60 ). The particles produce toxic effects according to their chemical and physical properties. The components of PM 10 and PM 2.5 can be organic (polycyclic aromatic hydrocarbons, dioxins, benzene, 1-3 butadiene) or inorganic (carbon, chlorides, nitrates, sulfates, metals) in nature ( 55 ).

Particulate Matter (PM) is divided into four main categories according to type and size ( 61 ) ( Table 2 ).

Table 2 . Types and sizes of particulate Matter (PM).

Gas contaminants include PM in aerial masses.

Particulate contaminants include contaminants such as smog, soot, tobacco smoke, oil smoke, fly ash, and cement dust.

Biological Contaminants are microorganisms (bacteria, viruses, fungi, mold, and bacterial spores), cat allergens, house dust and allergens, and pollen.

Types of Dust include suspended atmospheric dust, settling dust, and heavy dust.

Finally, another fact is that the half-lives of PM 10 and PM 2.5 particles in the atmosphere is extended due to their tiny dimensions; this permits their long-lasting suspension in the atmosphere and even their transfer and spread to distant destinations where people and the environment may be exposed to the same magnitude of pollution ( 53 ). They are able to change the nutrient balance in watery ecosystems, damage forests and crops, and acidify water bodies.

As stated, PM 2.5 , due to their tiny size, are causing more serious health effects. These aforementioned fine particles are the main cause of the “haze” formation in different metropolitan areas ( 12 , 13 , 61 ).

Ozone Impact in the Atmosphere

Ozone (O 3 ) is a gas formed from oxygen under high voltage electric discharge ( 62 ). It is a strong oxidant, 52% stronger than chlorine. It arises in the stratosphere, but it could also arise following chain reactions of photochemical smog in the troposphere ( 63 ).

Ozone can travel to distant areas from its initial source, moving with air masses ( 64 ). It is surprising that ozone levels over cities are low in contrast to the increased amounts occuring in urban areas, which could become harmful for cultures, forests, and vegetation ( 65 ) as it is reducing carbon assimilation ( 66 ). Ozone reduces growth and yield ( 47 , 48 ) and affects the plant microflora due to its antimicrobial capacity ( 67 , 68 ). In this regard, ozone acts upon other natural ecosystems, with microflora ( 69 , 70 ) and animal species changing their species composition ( 71 ). Ozone increases DNA damage in epidermal keratinocytes and leads to impaired cellular function ( 72 ).

Ground-level ozone (GLO) is generated through a chemical reaction between oxides of nitrogen and VOCs emitted from natural sources and/or following anthropogenic activities.

Ozone uptake usually occurs by inhalation. Ozone affects the upper layers of the skin and the tear ducts ( 73 ). A study of short-term exposure of mice to high levels of ozone showed malondialdehyde formation in the upper skin (epidermis) but also depletion in vitamins C and E. It is likely that ozone levels are not interfering with the skin barrier function and integrity to predispose to skin disease ( 74 ).

Due to the low water-solubility of ozone, inhaled ozone has the capacity to penetrate deeply into the lungs ( 75 ).

Toxic effects induced by ozone are registered in urban areas all over the world, causing biochemical, morphologic, functional, and immunological disorders ( 76 ).

The European project (APHEA2) focuses on the acute effects of ambient ozone concentrations on mortality ( 77 ). Daily ozone concentrations compared to the daily number of deaths were reported from different European cities for a 3-year period. During the warm period of the year, an observed increase in ozone concentration was associated with an increase in the daily number of deaths (0.33%), in the number of respiratory deaths (1.13%), and in the number of cardiovascular deaths (0.45%). No effect was observed during wintertime.

Carbon Monoxide (CO)

Carbon monoxide is produced by fossil fuel when combustion is incomplete. The symptoms of poisoning due to inhaling carbon monoxide include headache, dizziness, weakness, nausea, vomiting, and, finally, loss of consciousness.

The affinity of carbon monoxide to hemoglobin is much greater than that of oxygen. In this vein, serious poisoning may occur in people exposed to high levels of carbon monoxide for a long period of time. Due to the loss of oxygen as a result of the competitive binding of carbon monoxide, hypoxia, ischemia, and cardiovascular disease are observed.

Carbon monoxide affects the greenhouses gases that are tightly connected to global warming and climate. This should lead to an increase in soil and water temperatures, and extreme weather conditions or storms may occur ( 68 ).

However, in laboratory and field experiments, it has been seen to produce increased plant growth ( 78 ).

Nitrogen Oxide (NO 2 )

Nitrogen oxide is a traffic-related pollutant, as it is emitted from automobile motor engines ( 79 , 80 ). It is an irritant of the respiratory system as it penetrates deep in the lung, inducing respiratory diseases, coughing, wheezing, dyspnea, bronchospasm, and even pulmonary edema when inhaled at high levels. It seems that concentrations over 0.2 ppm produce these adverse effects in humans, while concentrations higher than 2.0 ppm affect T-lymphocytes, particularly the CD8+ cells and NK cells that produce our immune response ( 81 ).It is reported that long-term exposure to high levels of nitrogen dioxide can be responsible for chronic lung disease. Long-term exposure to NO 2 can impair the sense of smell ( 81 ).

However, systems other than respiratory ones can be involved, as symptoms such as eye, throat, and nose irritation have been registered ( 81 ).

High levels of nitrogen dioxide are deleterious to crops and vegetation, as they have been observed to reduce crop yield and plant growth efficiency. Moreover, NO 2 can reduce visibility and discolor fabrics ( 81 ).

Sulfur Dioxide (SO 2 )

Sulfur dioxide is a harmful gas that is emitted mainly from fossil fuel consumption or industrial activities. The annual standard for SO 2 is 0.03 ppm ( 82 ). It affects human, animal, and plant life. Susceptible people as those with lung disease, old people, and children, who present a higher risk of damage. The major health problems associated with sulfur dioxide emissions in industrialized areas are respiratory irritation, bronchitis, mucus production, and bronchospasm, as it is a sensory irritant and penetrates deep into the lung converted into bisulfite and interacting with sensory receptors, causing bronchoconstriction. Moreover, skin redness, damage to the eyes (lacrimation and corneal opacity) and mucous membranes, and worsening of pre-existing cardiovascular disease have been observed ( 81 ).

Environmental adverse effects, such as acidification of soil and acid rain, seem to be associated with sulfur dioxide emissions ( 83 ).

Lead is a heavy metal used in different industrial plants and emitted from some petrol motor engines, batteries, radiators, waste incinerators, and waste waters ( 84 ).

Moreover, major sources of lead pollution in the air are metals, ore, and piston-engine aircraft. Lead poisoning is a threat to public health due to its deleterious effects upon humans, animals, and the environment, especially in the developing countries.

Exposure to lead can occur through inhalation, ingestion, and dermal absorption. Trans- placental transport of lead was also reported, as lead passes through the placenta unencumbered ( 85 ). The younger the fetus is, the more harmful the toxic effects. Lead toxicity affects the fetal nervous system; edema or swelling of the brain is observed ( 86 ). Lead, when inhaled, accumulates in the blood, soft tissue, liver, lung, bones, and cardiovascular, nervous, and reproductive systems. Moreover, loss of concentration and memory, as well as muscle and joint pain, were observed in adults ( 85 , 86 ).

Children and newborns ( 87 ) are extremely susceptible even to minimal doses of lead, as it is a neurotoxicant and causes learning disabilities, impairment of memory, hyperactivity, and even mental retardation.

Elevated amounts of lead in the environment are harmful to plants and crop growth. Neurological effects are observed in vertebrates and animals in association with high lead levels ( 88 ).

Polycyclic Aromatic Hydrocarbons(PAHs)

The distribution of PAHs is ubiquitous in the environment, as the atmosphere is the most important means of their dispersal. They are found in coal and in tar sediments. Moreover, they are generated through incomplete combustion of organic matter as in the cases of forest fires, incineration, and engines ( 89 ). PAH compounds, such as benzopyrene, acenaphthylene, anthracene, and fluoranthene are recognized as toxic, mutagenic, and carcinogenic substances. They are an important risk factor for lung cancer ( 89 ).

Volatile Organic Compounds(VOCs)

Volatile organic compounds (VOCs), such as toluene, benzene, ethylbenzene, and xylene ( 90 ), have been found to be associated with cancer in humans ( 91 ). The use of new products and materials has actually resulted in increased concentrations of VOCs. VOCs pollute indoor air ( 90 ) and may have adverse effects on human health ( 91 ). Short-term and long-term adverse effects on human health are observed. VOCs are responsible for indoor air smells. Short-term exposure is found to cause irritation of eyes, nose, throat, and mucosal membranes, while those of long duration exposure include toxic reactions ( 92 ). Predictable assessment of the toxic effects of complex VOC mixtures is difficult to estimate, as these pollutants can have synergic, antagonistic, or indifferent effects ( 91 , 93 ).

Dioxins originate from industrial processes but also come from natural processes, such as forest fires and volcanic eruptions. They accumulate in foods such as meat and dairy products, fish and shellfish, and especially in the fatty tissue of animals ( 94 ).

Short-period exhibition to high dioxin concentrations may result in dark spots and lesions on the skin ( 94 ). Long-term exposure to dioxins can cause developmental problems, impairment of the immune, endocrine and nervous systems, reproductive infertility, and cancer ( 94 ).

Without any doubt, fossil fuel consumption is responsible for a sizeable part of air contamination. This contamination may be anthropogenic, as in agricultural and industrial processes or transportation, while contamination from natural sources is also possible. Interestingly, it is of note that the air quality standards established through the European Air Quality Directive are somewhat looser than the WHO guidelines, which are stricter ( 95 ).

Effect of Air Pollution on Health

The most common air pollutants are ground-level ozone and Particulates Matter (PM). Air pollution is distinguished into two main types:

Outdoor pollution is the ambient air pollution.

Indoor pollution is the pollution generated by household combustion of fuels.

People exposed to high concentrations of air pollutants experience disease symptoms and states of greater and lesser seriousness. These effects are grouped into short- and long-term effects affecting health.

Susceptible populations that need to be aware of health protection measures include old people, children, and people with diabetes and predisposing heart or lung disease, especially asthma.

As extensively stated previously, according to a recent epidemiological study from Harvard School of Public Health, the relative magnitudes of the short- and long-term effects have not been completely clarified ( 57 ) due to the different epidemiological methodologies and to the exposure errors. New models are proposed for assessing short- and long-term human exposure data more successfully ( 57 ). Thus, in the present section, we report the more common short- and long-term health effects but also general concerns for both types of effects, as these effects are often dependent on environmental conditions, dose, and individual susceptibility.

Short-term effects are temporary and range from simple discomfort, such as irritation of the eyes, nose, skin, throat, wheezing, coughing and chest tightness, and breathing difficulties, to more serious states, such as asthma, pneumonia, bronchitis, and lung and heart problems. Short-term exposure to air pollution can also cause headaches, nausea, and dizziness.

These problems can be aggravated by extended long-term exposure to the pollutants, which is harmful to the neurological, reproductive, and respiratory systems and causes cancer and even, rarely, deaths.

The long-term effects are chronic, lasting for years or the whole life and can even lead to death. Furthermore, the toxicity of several air pollutants may also induce a variety of cancers in the long term ( 96 ).

As stated already, respiratory disorders are closely associated with the inhalation of air pollutants. These pollutants will invade through the airways and will accumulate at the cells. Damage to target cells should be related to the pollutant component involved and its source and dose. Health effects are also closely dependent on country, area, season, and time. An extended exposure duration to the pollutant should incline to long-term health effects in relation also to the above factors.

Particulate Matter (PMs), dust, benzene, and O 3 cause serious damage to the respiratory system ( 97 ). Moreover, there is a supplementary risk in case of existing respiratory disease such as asthma ( 98 ). Long-term effects are more frequent in people with a predisposing disease state. When the trachea is contaminated by pollutants, voice alterations may be remarked after acute exposure. Chronic obstructive pulmonary disease (COPD) may be induced following air pollution, increasing morbidity and mortality ( 99 ). Long-term effects from traffic, industrial air pollution, and combustion of fuels are the major factors for COPD risk ( 99 ).

Multiple cardiovascular effects have been observed after exposure to air pollutants ( 100 ). Changes occurred in blood cells after long-term exposure may affect cardiac functionality. Coronary arteriosclerosis was reported following long-term exposure to traffic emissions ( 101 ), while short-term exposure is related to hypertension, stroke, myocardial infracts, and heart insufficiency. Ventricle hypertrophy is reported to occur in humans after long-time exposure to nitrogen oxide (NO 2 ) ( 102 , 103 ).

Neurological effects have been observed in adults and children after extended-term exposure to air pollutants.

Psychological complications, autism, retinopathy, fetal growth, and low birth weight seem to be related to long-term air pollution ( 83 ). The etiologic agent of the neurodegenerative diseases (Alzheimer's and Parkinson's) is not yet known, although it is believed that extended exposure to air pollution seems to be a factor. Specifically, pesticides and metals are cited as etiological factors, together with diet. The mechanisms in the development of neurodegenerative disease include oxidative stress, protein aggregation, inflammation, and mitochondrial impairment in neurons ( 104 ) ( Figure 1 ).

Figure 1 . Impact of air pollutants on the brain.

Brain inflammation was observed in dogs living in a highly polluted area in Mexico for a long period ( 105 ). In human adults, markers of systemic inflammation (IL-6 and fibrinogen) were found to be increased as an immediate response to PNC on the IL-6 level, possibly leading to the production of acute-phase proteins ( 106 ). The progression of atherosclerosis and oxidative stress seem to be the mechanisms involved in the neurological disturbances caused by long-term air pollution. Inflammation comes secondary to the oxidative stress and seems to be involved in the impairment of developmental maturation, affecting multiple organs ( 105 , 107 ). Similarly, other factors seem to be involved in the developmental maturation, which define the vulnerability to long-term air pollution. These include birthweight, maternal smoking, genetic background and socioeconomic environment, as well as education level.

However, diet, starting from breast-feeding, is another determinant factor. Diet is the main source of antioxidants, which play a key role in our protection against air pollutants ( 108 ). Antioxidants are free radical scavengers and limit the interaction of free radicals in the brain ( 108 ). Similarly, genetic background may result in a differential susceptibility toward the oxidative stress pathway ( 60 ). For example, antioxidant supplementation with vitamins C and E appears to modulate the effect of ozone in asthmatic children homozygous for the GSTM1 null allele ( 61 ). Inflammatory cytokines released in the periphery (e.g., respiratory epithelia) upregulate the innate immune Toll-like receptor 2. Such activation and the subsequent events leading to neurodegeneration have recently been observed in lung lavage in mice exposed to ambient Los Angeles (CA, USA) particulate matter ( 61 ). In children, neurodevelopmental morbidities were observed after lead exposure. These children developed aggressive and delinquent behavior, reduced intelligence, learning difficulties, and hyperactivity ( 109 ). No level of lead exposure seems to be “safe,” and the scientific community has asked the Centers for Disease Control and Prevention (CDC) to reduce the current screening guideline of 10 μg/dl ( 109 ).

It is important to state that impact on the immune system, causing dysfunction and neuroinflammation ( 104 ), is related to poor air quality. Yet, increases in serum levels of immunoglobulins (IgA, IgM) and the complement component C3 are observed ( 106 ). Another issue is that antigen presentation is affected by air pollutants, as there is an upregulation of costimulatory molecules such as CD80 and CD86 on macrophages ( 110 ).

As is known, skin is our shield against ultraviolet radiation (UVR) and other pollutants, as it is the most exterior layer of our body. Traffic-related pollutants, such as PAHs, VOCs, oxides, and PM, may cause pigmented spots on our skin ( 111 ). On the one hand, as already stated, when pollutants penetrate through the skin or are inhaled, damage to the organs is observed, as some of these pollutants are mutagenic and carcinogenic, and, specifically, they affect the liver and lung. On the other hand, air pollutants (and those in the troposphere) reduce the adverse effects of ultraviolet radiation UVR in polluted urban areas ( 111 ). Air pollutants absorbed by the human skin may contribute to skin aging, psoriasis, acne, urticaria, eczema, and atopic dermatitis ( 111 ), usually caused by exposure to oxides and photochemical smoke ( 111 ). Exposure to PM and cigarette smoking act as skin-aging agents, causing spots, dyschromia, and wrinkles. Lastly, pollutants have been associated with skin cancer ( 111 ).

Higher morbidity is reported to fetuses and children when exposed to the above dangers. Impairment in fetal growth, low birth weight, and autism have been reported ( 112 ).

Another exterior organ that may be affected is the eye. Contamination usually comes from suspended pollutants and may result in asymptomatic eye outcomes, irritation ( 112 ), retinopathy, or dry eye syndrome ( 113 , 114 ).

Environmental Impact of Air Pollution

Air pollution is harming not only human health but also the environment ( 115 ) in which we live. The most important environmental effects are as follows.

Acid rain is wet (rain, fog, snow) or dry (particulates and gas) precipitation containing toxic amounts of nitric and sulfuric acids. They are able to acidify the water and soil environments, damage trees and plantations, and even damage buildings and outdoor sculptures, constructions, and statues.

Haze is produced when fine particles are dispersed in the air and reduce the transparency of the atmosphere. It is caused by gas emissions in the air coming from industrial facilities, power plants, automobiles, and trucks.

Ozone , as discussed previously, occurs both at ground level and in the upper level (stratosphere) of the Earth's atmosphere. Stratospheric ozone is protecting us from the Sun's harmful ultraviolet (UV) rays. In contrast, ground-level ozone is harmful to human health and is a pollutant. Unfortunately, stratospheric ozone is gradually damaged by ozone-depleting substances (i.e., chemicals, pesticides, and aerosols). If this protecting stratospheric ozone layer is thinned, then UV radiation can reach our Earth, with harmful effects for human life (skin cancer) ( 116 ) and crops ( 117 ). In plants, ozone penetrates through the stomata, inducing them to close, which blocks CO 2 transfer and induces a reduction in photosynthesis ( 118 ).

Global climate change is an important issue that concerns mankind. As is known, the “greenhouse effect” keeps the Earth's temperature stable. Unhappily, anthropogenic activities have destroyed this protecting temperature effect by producing large amounts of greenhouse gases, and global warming is mounting, with harmful effects on human health, animals, forests, wildlife, agriculture, and the water environment. A report states that global warming is adding to the health risks of poor people ( 119 ).

People living in poorly constructed buildings in warm-climate countries are at high risk for heat-related health problems as temperatures mount ( 119 ).

Wildlife is burdened by toxic pollutants coming from the air, soil, or the water ecosystem and, in this way, animals can develop health problems when exposed to high levels of pollutants. Reproductive failure and birth effects have been reported.

Eutrophication is occurring when elevated concentrations of nutrients (especially nitrogen) stimulate the blooming of aquatic algae, which can cause a disequilibration in the diversity of fish and their deaths.

Without a doubt, there is a critical concentration of pollution that an ecosystem can tolerate without being destroyed, which is associated with the ecosystem's capacity to neutralize acidity. The Canada Acid Rain Program established this load at 20 kg/ha/yr ( 120 ).

Hence, air pollution has deleterious effects on both soil and water ( 121 ). Concerning PM as an air pollutant, its impact on crop yield and food productivity has been reported. Its impact on watery bodies is associated with the survival of living organisms and fishes and their productivity potential ( 121 ).

An impairment in photosynthetic rhythm and metabolism is observed in plants exposed to the effects of ozone ( 121 ).

Sulfur and nitrogen oxides are involved in the formation of acid rain and are harmful to plants and marine organisms.

Last but not least, as mentioned above, the toxicity associated with lead and other metals is the main threat to our ecosystems (air, water, and soil) and living creatures ( 121 ).

In 2018, during the first WHO Global Conference on Air Pollution and Health, the WHO's General Director, Dr. Tedros Adhanom Ghebreyesus, called air pollution a “silent public health emergency” and “the new tobacco” ( 122 ).

Undoubtedly, children are particularly vulnerable to air pollution, especially during their development. Air pollution has adverse effects on our lives in many different respects.

Diseases associated with air pollution have not only an important economic impact but also a societal impact due to absences from productive work and school.

Despite the difficulty of eradicating the problem of anthropogenic environmental pollution, a successful solution could be envisaged as a tight collaboration of authorities, bodies, and doctors to regularize the situation. Governments should spread sufficient information and educate people and should involve professionals in these issues so as to control the emergence of the problem successfully.

Technologies to reduce air pollution at the source must be established and should be used in all industries and power plants. The Kyoto Protocol of 1997 set as a major target the reduction of GHG emissions to below 5% by 2012 ( 123 ). This was followed by the Copenhagen summit, 2009 ( 124 ), and then the Durban summit of 2011 ( 125 ), where it was decided to keep to the same line of action. The Kyoto protocol and the subsequent ones were ratified by many countries. Among the pioneers who adopted this important protocol for the world's environmental and climate “health” was China ( 3 ). As is known, China is a fast-developing economy and its GDP (Gross Domestic Product) is expected to be very high by 2050, which is defined as the year of dissolution of the protocol for the decrease in gas emissions.

A more recent international agreement of crucial importance for climate change is the Paris Agreement of 2015, issued by the UNFCCC (United Nations Climate Change Committee). This latest agreement was ratified by a plethora of UN (United Nations) countries as well as the countries of the European Union ( 126 ). In this vein, parties should promote actions and measures to enhance numerous aspects around the subject. Boosting education, training, public awareness, and public participation are some of the relevant actions for maximizing the opportunities to achieve the targets and goals on the crucial matter of climate change and environmental pollution ( 126 ). Without any doubt, technological improvements makes our world easier and it seems difficult to reduce the harmful impact caused by gas emissions, we could limit its use by seeking reliable approaches.

Synopsizing, a global prevention policy should be designed in order to combat anthropogenic air pollution as a complement to the correct handling of the adverse health effects associated with air pollution. Sustainable development practices should be applied, together with information coming from research in order to handle the problem effectively.

At this point, international cooperation in terms of research, development, administration policy, monitoring, and politics is vital for effective pollution control. Legislation concerning air pollution must be aligned and updated, and policy makers should propose the design of a powerful tool of environmental and health protection. As a result, the main proposal of this essay is that we should focus on fostering local structures to promote experience and practice and extrapolate these to the international level through developing effective policies for sustainable management of ecosystems.

Author Contributions

All authors listed have made a substantial, direct and intellectual contribution to the work, and approved it for publication.

Conflict of Interest

IM is employed by the company Delphis S.A.

The remaining authors declare that the present review paper was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

1. WHO. Air Pollution . WHO. Available online at: http://www.who.int/airpollution/en/ (accessed October 5, 2019).

Google Scholar

2. Moores FC. Climate change and air pollution: exploring the synergies and potential for mitigation in industrializing countries. Sustainability . (2009) 1:43–54. doi: 10.3390/su1010043

CrossRef Full Text | Google Scholar

3. USGCRP (2009). Global Climate Change Impacts in the United States. In: Karl TR, Melillo JM, Peterson TC, editors. Climate Change Impacts by Sectors: Ecosystems . New York, NY: United States Global Change Research Program. Cambridge University Press.

4. Marlon JR, Bloodhart B, Ballew MT, Rolfe-Redding J, Roser-Renouf C, Leiserowitz A, et al. (2019). How hope and doubt affect climate change mobilization. Front. Commun. 4:20. doi: 10.3389/fcomm.2019.00020

5. Eze IC, Schaffner E, Fischer E, Schikowski T, Adam M, Imboden M, et al. Long- term air pollution exposure and diabetes in a population-based Swiss cohort. Environ Int . (2014) 70:95–105. doi: 10.1016/j.envint.2014.05.014

PubMed Abstract | CrossRef Full Text | Google Scholar

6. Kelishadi R, Poursafa P. Air pollution and non-respiratory health hazards for children. Arch Med Sci . (2010) 6:483–95. doi: 10.5114/aoms.2010.14458

7. Manucci PM, Franchini M. Health effects of ambient air pollution in developing countries. Int J Environ Res Public Health . (2017) 14:1048. doi: 10.3390/ijerph14091048

8. Burden of Disease from Ambient and Household Air Pollution . Available online: http://who.int/phe/health_topics/outdoorair/databases/en/ (accessed August 15, 2017).

9. Hashim D, Boffetta P. Occupational and environmental exposures and cancers in developing countries. Ann Glob Health . (2014) 80:393–411. doi: 10.1016/j.aogh.2014.10.002

10. Guo Y, Zeng H, Zheng R, Li S, Pereira G, Liu Q, et al. The burden of lung cancer mortality attributable to fine particles in China. Total Environ Sci . (2017) 579:1460–6. doi: 10.1016/j.scitotenv.2016.11.147

11. Hou Q, An XQ, Wang Y, Guo JP. An evaluation of resident exposure to respirable particulate matter and health economic loss in Beijing during Beijing 2008 Olympic Games. Sci Total Environ . (2010) 408:4026–32. doi: 10.1016/j.scitotenv.2009.12.030

12. Kan H, Chen R, Tong S. Ambient air pollution, climate change, and population health in China. Environ Int . (2012) 42:10–9. doi: 10.1016/j.envint.2011.03.003

13. Burroughs Peña MS, Rollins A. Environmental exposures and cardiovascular disease: a challenge for health and development in low- and middle-income countries. Cardiol Clin . (2017) 35:71–86. doi: 10.1016/j.ccl.2016.09.001

14. Kankaria A, Nongkynrih B, Gupta S. Indoor air pollution in india: implications on health and its control. Indian J Comm Med . 39:203–7. doi: 10.4103/0970-0218.143019

15. Parajuli I, Lee H, Shrestha KR. Indoor air quality and ventilation assessment of rural mountainous households of Nepal. Int J Sust Built Env . (2016) 5:301–11. doi: 10.1016/j.ijsbe.2016.08.003

16. Saud T, Gautam R, Mandal TK, Gadi R, Singh DP, Sharma SK. Emission estimates of organic and elemental carbon from household biomass fuel used over the Indo-Gangetic Plain (IGP), India. Atmos Environ . (2012) 61:212–20. doi: 10.1016/j.atmosenv.2012.07.030

17. Singh DP, Gadi R, Mandal TK, Saud T, Saxena M, Sharma SK. Emissions estimates of PAH from biomass fuels used in rural sector of Indo-Gangetic Plains of India. Atmos Environ . (2013) 68:120–6. doi: 10.1016/j.atmosenv.2012.11.042

18. Dherani M, Pope D, Mascarenhas M, Smith KR, Weber M BN. Indoor air pollution from unprocessed solid fuel use and pneumonia risk in children aged under five years: a systematic review and meta-analysis. Bull World Health Organ . (2008) 86:390–4. doi: 10.2471/BLT.07.044529

19. Kassomenos P, Kelessis A, Petrakakis M, Zoumakis N, Christides T, Paschalidou AK. Air Quality assessment in a heavily-polluted urban Mediterranean environment through Air Quality indices. Ecol Indic . (2012) 18:259–68. doi: 10.1016/j.ecolind.2011.11.021

20. Dockery DW, Pope CA, Xu X, Spengler JD, Ware JH, Fay ME, et al. An association between air pollution and mortality in six U.S. cities. N Engl J Med . (1993) 329:1753–9. doi: 10.1056/NEJM199312093292401

21. Schwela DH, Köth-Jahr I. Leitfaden für die Aufstellung von Luftreinhalteplänen [Guidelines for the Implementation of Clean Air Implementation Plans]. Landesumweltamt des Landes Nordrhein Westfalen. State Environmental Service of the State of North Rhine-Westphalia (1994).

22. Newlands M. Environmental Activism, Environmental Politics, and Representation: The Framing of the British Environmental Activist Movement . Ph.D. thesis. University of East London, United Kingdom (2015).

23. NEPIS (National Service Center for Environmental Publications) US EPA (Environmental Protection Agency) (2017). Available online at: https://www.epa.gov/clean-air-act-overview/air-pollution-current-and-future-challenges (accessed August 15, 2017).

24. NRC (National Research Council). Available online at: https://www.nap.edu/read/10728/chapter/1,2014 (accessed September 17, 2019).

25. Bull A. Traffic Congestion: The Problem and How to Deal With It . Santiago: Nationes Unidas, Cepal (2003).

26. Spiegel J, Maystre LY. Environmental Pollution Control, Part VII - The Environment, Chapter 55, Encyclopedia of Occupational Health and Safety . Available online at: http://www.ilocis.org/documents/chpt55e.htm (accessed September 17, 2019).

27. European Community Reports. Assessment of the Effectiveness of European Air Quality Policies and Measures: Case Study 2; Comparison of the EU and US Air Quality Standards and Planning Requirements. (2004). Available online at: https://ec.europa.eu/environment/archives/cafe/activities/pdf/case_study2.pdf (accessed September 22, 2019).

28. Gibson R, Ward S. Parties in the digital age; a review. J Represent Democracy . (2009) 45:87–100. doi: 10.1080/00344890802710888

29. Kaun A, Uldam J. Digital activism: after the hype. New Media Soc. (2017) 20:2099–106. doi: 10.1177/14614448177319

30. Sivitanides M, Shah V. The era of digital activism. In: 2011 Conference for Information Systems Applied Research(CONISAR) Proceedings Wilmington North Carolina, USA . Available online at: https://www.arifyildirim.com/ilt510/marcos.sivitanides.vivek.shah.pdf (accessed September 22, 2019).

31. Möller L, Schuetzle D, Autrup H. Future research needs associated with the assessment of potential human health risks from exposure to toxic ambient air pollutants. Environ Health Perspect . (1994) 102(Suppl. 4):193–210. doi: 10.1289/ehp.94102s4193

32. Jacobson MZ, Jacobson PMZ. Atmospheric Pollution: History, Science, and Regulation. Cambridge University Press (2002). p. 206. doi: 10.1256/wea.243.02

33. Stover RH. Flooding of soil for disease control. In: Mulder D, editor. Chapter 3. Developments in Agricultural and Managed Forest Ecology . Elsevier (1979). p. 19–28. Available online at: http://www.sciencedirect.com/science/article/pii/B9780444416926500094 doi: 10.1016/B978-0-444-41692-6.50009-4 (accessed July 1, 2019).

34. Maipa V, Alamanos Y, Bezirtzoglou E. Seasonal fluctuation of bacterial indicators in coastal waters. Microb Ecol Health Dis . (2001) 13:143–6. doi: 10.1080/089106001750462687

35. Bezirtzoglou E, Dimitriou D, Panagiou A. Occurrence of Clostridium perfringens in river water by using a new procedure. Anaerobe . (1996) 2:169–73. doi: 10.1006/anae.1996.0022

36. Kjellstrom T, Lodh M, McMichael T, Ranmuthugala G, Shrestha R, Kingsland S. Air and Water Pollution: Burden and Strategies for Control. DCP, Chapter 43. 817–32 p. Available online at: https://www.dcp-3.org/sites/default/files/dcp2/DCP43.pdf (accessed September 17, 2017).

37. Pathak RK, Wang T, Ho KF, Lee SC. Characteristics of summertime PM2.5 organic and elemental carbon in four major Chinese cities: implications of high acidity for water- soluble organic carbon (WSOC). Atmos Environ . (2011) 45:318–25. doi: 10.1016/j.atmosenv.2010.10.021

38. Bonavigo L, Zucchetti M, Mankolli H. Water radioactive pollution and related environmental aspects. J Int Env Appl Sci . (2009) 4:357–63

39. World Health Organization (WHO). Preventing Disease Through Healthy Environments: Towards an Estimate of the Environmental Burden of Disease . 1106 p. Available online at: https://www.who.int/quantifying_ehimpacts/publications/preventingdisease.pdf (accessed September 22, 2019).

40. Stansfeld SA. Noise effects on health in the context of air pollution exposure. Int J Environ Res Public Health . (2015) 12:12735–60. doi: 10.3390/ijerph121012735

41. Ethical Unicorn. Everything You Need To Know About Aerosols & Air Pollution. (2019). Available online at: https://ethicalunicorn.com/2019/04/29/everything-you-need-to-know-about-aerosols-air-pollution/ (accessed October 4, 2019).

42. Colbeck I, Lazaridis M. Aerosols and environmental pollution. Sci Nat . (2009) 97:117–31. doi: 10.1007/s00114-009-0594-x

43. Incecik S, Gertler A, Kassomenos P. Aerosols and air quality. Sci Total Env . (2014) 355, 488–9. doi: 10.1016/j.scitotenv.2014.04.012

44. D'Amato G, Pawankar R, Vitale C, Maurizia L. Climate change and air pollution: effects on respiratory allergy. Allergy Asthma Immunol Res . (2016) 8:391–5. doi: 10.4168/aair.2016.8.5.391

45. Bezirtzoglou C, Dekas K, Charvalos E. Climate changes, environment and infection: facts, scenarios and growing awareness from the public health community within Europe. Anaerobe . (2011) 17:337–40. doi: 10.1016/j.anaerobe.2011.05.016

46. Castelli F, Sulis G. Migration and infectious diseases. Clin Microbiol Infect . (2017) 23:283–9. doi: 10.1016/j.cmi.2017.03.012

47. Watson JT, Gayer M, Connolly MA. Epidemics after natural disasters. Emerg Infect Dis . (2007) 13:1–5. doi: 10.3201/eid1301.060779

48. Fenn B. Malnutrition in Humanitarian Emergencies . Available online at: https://www.who.int/diseasecontrol_emergencies/publications/idhe_2009_london_malnutrition_fenn.pdf . (accessed August 15, 2017).

49. Lindh E, Argentini C, Remoli ME, Fortuna C, Faggioni G, Benedetti E, et al. The Italian 2017 outbreak Chikungunya virus belongs to an emerging Aedes albopictus –adapted virus cluster introduced from the Indian subcontinent. Open Forum Infect Dis. (2019) 6:ofy321. doi: 10.1093/ofid/ofy321

50. Calba C, Guerbois-Galla M, Franke F, Jeannin C, Auzet-Caillaud M, Grard G, Pigaglio L, Decoppet A, et al. Preliminary report of an autochthonous chikungunya outbreak in France, July to September 2017. Eur Surveill . (2017) 22:17-00647. doi: 10.2807/1560-7917.ES.2017.22.39.17-00647

51. Menne B, Murray V. Floods in the WHO European Region: Health Effects and Their Prevention . Copenhagen: WHO; Weltgesundheits organisation, Regionalbüro für Europa (2013). Available online at: http://www.euro.who.int/data/assets/pdf_file/0020/189020/e96853.pdf (accessed 15 August 2017).

52. Schneider SH. The greenhouse effect: science and policy. Science . (1989) 243:771–81. doi: 10.1126/science.243.4892.771

53. Wilson WE, Suh HH. Fine particles and coarse particles: concentration relationships relevant to epidemiologic studies. J Air Waste Manag Assoc . (1997) 47:1238–49. doi: 10.1080/10473289.1997.10464074

54. US EPA (US Environmental Protection Agency) (2018). Available online at: https://www.epa.gov/pm-pollution/particulate-matter-pm-basics (accessed September 22, 2018).

55. Cheung K, Daher N, Kam W, Shafer MM, Ning Z, Schauer JJ, et al. Spatial and temporal variation of chemical composition and mass closure of ambient coarse particulate matter (PM10–2.5) in the Los Angeles area. Atmos Environ . (2011) 45:2651–62. doi: 10.1016/j.atmosenv.2011.02.066

56. Zhang L, Yang Y, Li Y, Qian ZM, Xiao W, Wang X, et al. Short-term and long-term effects of PM2.5 on acute nasopharyngitis in 10 communities of Guangdong, China. Sci Total Env. (2019) 688:136–42. doi: 10.1016/j.scitotenv.2019.05.470.

57. Kloog I, Ridgway B, Koutrakis P, Coull BA, Schwartz JD. Long- and short-term exposure to PM2.5 and mortality using novel exposure models, Epidemiology . (2013) 24:555–61. doi: 10.1097/EDE.0b013e318294beaa

58. New Hampshire Department of Environmental Services. Current and Forecasted Air Quality in New Hampshire . Environmental Fact Sheet (2019). Available online at: https://www.des.nh.gov/organization/commissioner/pip/factsheets/ard/documents/ard-16.pdf (accessed September 22, 2019).

59. Kappos AD, Bruckmann P, Eikmann T, Englert N, Heinrich U, Höppe P, et al. Health effects of particles in ambient air. Int J Hyg Environ Health . (2004) 207:399–407. doi: 10.1078/1438-4639-00306

60. Boschi N (Ed.). Defining an educational framework for indoor air sciences education. In: Education and Training in Indoor Air Sciences . Luxembourg: Springer Science & Business Media (2012). 245 p.

61. Heal MR, Kumar P, Harrison RM. Particles, air quality, policy and health. Chem Soc Rev . (2012) 41:6606–30. doi: 10.1039/c2cs35076a

62. Bezirtzoglou E, Alexopoulos A. Ozone history and ecosystems: a goliath from impacts to advance industrial benefits and interests, to environmental and therapeutical strategies. In: Ozone Depletion, Chemistry and Impacts. (2009). p. 135–45.

63. Villányi V, Turk B, Franc B, Csintalan Z. Ozone Pollution and its Bioindication. In: Villányi V, editor. Air Pollution . London: Intech Open (2010). doi: 10.5772/10047

64. Massachusetts Department of Public Health. Massachusetts State Health Assessment . Boston, MA (2017). Available online at: https://www.mass.gov/files/documents/2017/11/03/2017%20MA%20SHA%20final%20compressed.pdf (accessed October 30, 2017).

65. Lorenzini G, Saitanis C. Ozone: A Novel Plant “Pathogen.” In: Sanitá di Toppi L, Pawlik-Skowrońska B, editors. Abiotic Stresses in Plant Springer Link (2003). p. 205–29. doi: 10.1007/978-94-017-0255-3_8

66. Fares S, Vargas R, Detto M, Goldstein AH, Karlik J, Paoletti E, et al. Tropospheric ozone reduces carbon assimilation in trees: estimates from analysis of continuous flux measurements. Glob Change Biol . (2013) 19:2427–43. doi: 10.1111/gcb.12222

67. Harmens H, Mills G, Hayes F, Jones L, Norris D, Fuhrer J. Air Pollution and Vegetation . ICP Vegetation Annual Report 2006/2007. (2012)

68. Emberson LD, Pleijel H, Ainsworth EA, den Berg M, Ren W, Osborne S, et al. Ozone effects on crops and consideration in crop models. Eur J Agron . (2018) 100:19–34. doi: 10.1016/j.eja.2018.06.002

69. Alexopoulos A, Plessas S, Ceciu S, Lazar V, Mantzourani I, Voidarou C, et al. Evaluation of ozone efficacy on the reduction of microbial population of fresh cut lettuce ( Lactuca sativa ) and green bell pepper ( Capsicum annuum ). Food Control . (2013) 30:491–6. doi: 10.1016/j.foodcont.2012.09.018

70. Alexopoulos A, Plessas S, Kourkoutas Y, Stefanis C, Vavias S, Voidarou C, et al. Experimental effect of ozone upon the microbial flora of commercially produced dairy fermented products. Int J Food Microbiol . (2017) 246:5–11. doi: 10.1016/j.ijfoodmicro.2017.01.018

71. Maggio A, Fagnano M. Ozone damages to mediterranean crops: physiological responses. Ital J Agron . (2008) 13–20. doi: 10.4081/ija.2008.13

72. McCarthy JT, Pelle E, Dong K, Brahmbhatt K, Yarosh D, Pernodet N. Effects of ozone in normal human epidermal keratinocytes. Exp Dermatol . (2013) 22:360–1. doi: 10.1111/exd.12125

73. WHO. Health Risks of Ozone From Long-Range Transboundary Air Pollution . Available online at: http://www.euro.who.int/data/assets/pdf_file/0005/78647/E91843.pdf (accessed August 15, 2019).

74. Thiele JJ, Traber MG, Tsang K, Cross CE, Packer L. In vivo exposure to ozone depletes vitamins C and E and induces lipid peroxidation in epidermal layers of murine skin. Free Radic Biol Med. (1997) 23:365–91. doi: 10.1016/S0891-5849(96)00617-X

75. Hatch GE, Slade R, Harris LP, McDonnell WF, Devlin RB, Koren HS, et al. Ozone dose and effect in humans and rats. A comparison using oxygen- 18 labeling and bronchoalveolar lavage. Am J Respir Crit Care Med . (1994) 150:676–83. doi: 10.1164/ajrccm.150.3.8087337

76. Lippmann M. Health effects of ozone. A critical review. JAPCA . (1989) 39:672–95. doi: 10.1080/08940630.1989.10466554

77. Gryparis A, Forsberg B, Katsouyanni K, Analitis A, Touloumi G, Schwartz J, et al. Acute effects of ozone on mortality from the “air pollution and health: a European approach” project. Am J Respir Crit Care Med . (2004) 170:1080–7. doi: 10.1164/rccm.200403-333OC

78. Soon W, Baliunas SL, Robinson AB, Robinson ZW. Environmental effects of increased atmospheric carbon dioxide. Climate Res . (1999) 13:149–64 doi: 10.1260/0958305991499694

79. Richmont-Bryant J, Owen RC, Graham S, Snyder M, McDow S, Oakes M, et al. Estimation of on-road NO2 concentrations, NO2/NOX ratios, and related roadway gradients from near-road monitoring data. Air Qual Atm Health . (2017) 10:611–25. doi: 10.1007/s11869-016-0455-7

80. Hesterberg TW, Bunn WB, McClellan RO, Hamade AK, Long CM, Valberg PA. Critical review of the human data on short-term nitrogen dioxide (NO 2 ) exposures: evidence for NO2 no-effect levels. Crit Rev Toxicol . (2009) 39:743–81. doi: 10.3109/10408440903294945

81. Chen T-M, Gokhale J, Shofer S, Kuschner WG. Outdoor air pollution: nitrogen dioxide, sulfur dioxide, and carbon monoxide health effects. Am J Med Sci . (2007) 333:249–56. doi: 10.1097/MAJ.0b013e31803b900f

82. US EPA. Table of Historical SO 2 NAAQS, Sulfur US EPA . Available online at: https://www3.epa.gov/ttn/naaqs/standards/so2/s_so2_history.html (accessed October 5, 2019).

83. WHO Regional Office of Europe (2000). Available online at: https://euro.who.int/_data/assets/pdf_file/0020/123086/AQG2ndEd_7_4Sulfuroxide.pdf

84. Pruss-Ustun A, Fewrell L, Landrigan PJ, Ayuso-Mateos JL. Lead exposure. Comparative Quantification of Health Risks . World Health Organization. p. 1495–1542. Available online at: https://www.who.int/publications/cra/chapters/volume2/1495-1542.pdf?ua=1

PubMed Abstract | Google Scholar

85. Goyer RA. Transplacental transport of lead. Environ Health Perspect . (1990) 89:101–5. doi: 10.1289/ehp.9089101

86. National Institute of Environmental Health Sciences (NIH). Lead and Your Health . (2013). 1–4 p. Available online at: https://www.niehs.nih.gov/health/materials/lead_and_your_health_508.pdf (accessed September 17, 2019).

87. Farhat A, Mohammadzadeh A, Balali-Mood M, Aghajanpoor-Pasha M, Ravanshad Y. Correlation of blood lead level in mothers and exclusively breastfed infants: a study on infants aged less than six months. Asia Pac J Med Toxicol . (2013) 2:150–2.

88. Assi MA, Hezmee MNM, Haron AW, Sabri MYM, Rajion MA. The detrimental effects of lead on human and animal health. Vet World . (2016) 9:660–71. doi: 10.14202/vetworld.2016.660-671

89. Abdel-Shafy HI, Mansour MSM. A review on polycyclic aromatic hydrocarbons: source, environmental impact, effect on human health and remediation. Egypt J Pet . (2016) 25:107–23. doi: 10.1016/j.ejpe.2015.03.011

90. Kumar A, Singh BP, Punia M, Singh D, Kumar K, Jain VK. Assessment of indoor air concentrations of VOCs and their associated health risks in the library of Jawaharlal Nehru University, New Delhi. Environ Sci Pollut Res Int . (2014) 21:2240–8. doi: 10.1007/s11356-013-2150-7

91. Molhave L, Clausen G, Berglund B, Ceaurriz J, Kettrup A, Lindvall T, et al. Total Volatile Organic Compounds (TVOC) in Indoor Air Quality Investigations. Indoor Air . 7:225–240. doi: 10.1111/j.1600-0668.1997.00002.x

92. Gibb T. Indoor Air Quality May be Hazardous to Your Health . MSU Extension. Available online at: https://www.canr.msu.edu/news/indoor_air_quality_may_be_hazardous_to_your_health (accessed October 5, 2019).

93. Ebersviller S, Lichtveld K, Sexton KG, Zavala J, Lin Y-H, Jaspers I, et al. Gaseous VOCs rapidly modify particulate matter and its biological effects – Part 1: simple VOCs and model PM. Atmos Chem Phys Discuss . (2012) 12:5065–105. doi: 10.5194/acpd-12-5065-2012

94. WHO (World Health Organization). Dioxins and Their Effects on Human Health. Available online at: https://www.who.int/news-room/fact-sheets/detail/dioxins-and-their-effects-on-human-health (accessed October 5, 2019).

95. EEA (European Environmental Agency). Air Quality Standards to the European Union and WHO . Available online at: https://www.eea.europa.eu/themes/data-and-maps/figures/air-quality-standards-under-the

96. Nakano T, Otsuki T. [Environmental air pollutants and the risk of cancer]. (Japanese). Gan To Kagaku Ryoho . (2013) 40:1441–5.

97. Kurt OK, Zhang J, Pinkerton KE. Pulmonary health effects of air pollution. Curr Opin Pulm Med . (2016) 22:138–43. doi: 10.1097/MCP.0000000000000248

98. Guarnieri M, Balmes JR. Outdoor air pollution and asthma. Lancet . (2014) 383:1581–92. doi: 10.1016/S0140-6736(14)60617-6

99. Jiang X-Q, Mei X-D, Feng D. Air pollution and chronic airway diseases: what should people know and do? J Thorac Dis . (2016) 8:E31–40.

100. Bourdrel T, Bind M-A, Béjot Y, Morel O, Argacha J-F. Cardiovascular effects of air pollution. Arch Cardiovasc Dis . (2017) 110:634–42. doi: 10.1016/j.acvd.2017.05.003

101. Hoffmann B, Moebus S, Möhlenkamp S, Stang A, Lehmann N, Dragano N, et al. Residential exposure to traffic is associated with coronary atherosclerosis. Circulation . (2007) 116:489–496. doi: 10.1161/CIRCULATIONAHA.107.693622

102. Katholi RE, Couri DM. Left ventricular hypertrophy: major risk factor in patients with hypertension: update and practical clinical applications. Int J Hypertens . (2011) 2011:495349. doi: 10.4061/2011/495349

103. Leary PJ, Kaufman JD, Barr RG, Bluemke DA, Curl CL, Hough CL, et al. Traffic- related air pollution and the right ventricle. the multi-ethnic study of atherosclerosis. Am J Respir Crit Care Med . (2014) 189:1093–100. doi: 10.1164/rccm.201312-2298OC

104. Genc S, Zadeoglulari Z, Fuss SH, Genc K. The adverse effects of air pollution on the nervous system. J Toxicol . (2012) 2012:782462. doi: 10.1155/2012/782462

105. Calderon-Garciduenas L, Azzarelli B, Acuna H, et al. Air pollution and brain damage. Toxicol Pathol. (2002) 30:373–89. doi: 10.1080/01926230252929954

106. Rückerl R, Greven S, Ljungman P, Aalto P, Antoniades C, Bellander T, et al. Air pollution and inflammation (interleukin-6, C-reactive protein, fibrinogen) in myocardial infarction survivors. Environ Health Perspect . (2007) 115:1072–80. doi: 10.1289/ehp.10021

107. Peters A, Veronesi B, Calderón-Garcidueñas L, Gehr P, Chen LC, Geiser M, et al. Translocation and potential neurological effects of fine and ultrafine particles a critical update. Part Fibre Toxicol . (2006) 3:13–8. doi: 10.1186/1743-8977-3-13

108. Kelly FJ. Dietary antioxidants and environmental stress. Proc Nutr Soc . (2004) 63:579–85. doi: 10.1079/PNS2004388

109. Bellinger DC. Very low lead exposures and children's neurodevelopment. Curr Opin Pediatr . (2008) 20:172–7. doi: 10.1097/MOP.0b013e3282f4f97b

110. Balbo P, Silvestri M, Rossi GA, Crimi E, Burastero SE. Differential role of CD80 and CD86 on alveolar macrophages in the presentation of allergen to T lymphocytes in asthma. Clin Exp Allergy J Br Soc Allergy Clin Immunol . (2001) 31:625–36. doi: 10.1046/j.1365-2222.2001.01068.x

111. Drakaki E, Dessinioti C, Antoniou C. Air pollution and the skin. Front Environ Sci Eng China . (2014) 15:2–8. doi: 10.3389/fenvs.2014.00011

112. Weisskopf MG, Kioumourtzoglou M-A, Roberts AL. Air pollution and autism spectrum disorders: causal or confounded? Curr Environ Health Rep . (2015) 2:430–9. doi: 10.1007/s40572-015-0073-9

113. Mo Z, Fu Q, Lyu D, Zhang L, Qin Z, Tang Q, et al. Impacts of air pollution on dry eye disease among residents in Hangzhou, China: a case-crossover study. Environ Pollut . (2019) 246:183–9. doi: 10.1016/j.envpol.2018.11.109

114. Klopfer J. Effects of environmental air pollution on the eye. J Am Optom Assoc . (1989) 60:773–8.

115. Ashfaq A, Sharma P. Environmental effects of air pollution and application of engineered methods to combat the problem. J Indust Pollut Control . (2012) 29.

116. Madronich S, de Gruijl F. Skin cancer and UV radiation. Nature . (1993) 366:23–9. doi: 10.1038/366023a0

117. Teramura A. Effects of UV-B radiation on the growth and yield of crop plants. Physiol Plant . (2006) 58:415–27. doi: 10.1111/j.1399-3054.1983.tb04203.x

118. Singh E, Tiwari S, Agrawal M. Effects of elevated ozone on photosynthesis and stomatal conductance of two soybean varieties: a case study to assess impacts of one component of predicted global climate change. Plant Biol Stuttg Ger . (2009) 11(Suppl. 1):101–8. doi: 10.1111/j.1438-8677.2009.00263.x

119. Manderson L. How global Warming is Adding to the Health Risks of Poor People . The Conversation. University of the Witwatersrand. Available online at: http://theconversation.com/how-global-warming-is-adding-to-the-health-risks-of-poor-people-109520 (accessed October 5, 2019).

120. Ministers of Energy and Environment. Federal/Provincial/Territorial Ministers of Energy and Environment (Canada), editor. The Canada-Wide Acid Rain Strategy for Post-2000 . Halifax: The Ministers (1999). 11 p.

121. Zuhara S, Isaifan R. The impact of criteria air pollutants on soil and water: a review. (2018) 278–84. doi: 10.30799/jespr.133.18040205

122. WHO. First WHO Global Conference on Air Pollution and Health. (2018). Available online at: https://www.who.int/airpollution/events/conference/en/ (accessed October 6, 2019).

123. What is the Kyoto Protocol? UNFCCC . Available online at: https://unfccc.int/kyoto__protocol (accessed October 6, 2019).

124. CopenhagenClimate Change Conference (UNFCCC) . Available online at: https://unfccc.int/process-and-meetings/conferences/past-conferences/copenhagen-climate-change-conference-december-2009/copenhagen-climate-change-conference-december-2009 (accessed October 6, 2019).

125. Durban Climate Change Conference,. UNFCCC (2011). Available online at: https://unfccc.int/process-and-meetings/conferences/past-conferences/copenhagen-climate-change-conference-december-2009/copenhagen-climate-change-conference-december-2009 (accessed October 6, 2019).

126. Paris Climate Change Agreement,. (2016). Available online at: https://unfccc.int/process-and-meetings/the-paris-agreement/the-paris-agreement

Keywords: air pollution, environment, health, public health, gas emission, policy

Citation: Manisalidis I, Stavropoulou E, Stavropoulos A and Bezirtzoglou E (2020) Environmental and Health Impacts of Air Pollution: A Review. Front. Public Health 8:14. doi: 10.3389/fpubh.2020.00014

Received: 17 October 2019; Accepted: 17 January 2020; Published: 20 February 2020.

Reviewed by:

Copyright © 2020 Manisalidis, Stavropoulou, Stavropoulos and Bezirtzoglou. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY) . The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

*Correspondence: Ioannis Manisalidis, giannismanisal@gmail.com ; Elisavet Stavropoulou, elisabeth.stavropoulou@gmail.com

† These authors have contributed equally to this work

Disclaimer: All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article or claim that may be made by its manufacturer is not guaranteed or endorsed by the publisher.

An official website of the United States government

The .gov means it’s official. Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

The site is secure. The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

• Publications
• Account settings

The PMC website is updating on October 15, 2024. Learn More or Try it out now .

• Advanced Search
• Journal List
• Springer Nature - PMC COVID-19 Collection

A review of the global climate change impacts, adaptation, and sustainable mitigation measures

Kashif abbass.

1 School of Economics and Management, Nanjing University of Science and Technology, Nanjing, 210094 People’s Republic of China

Muhammad Zeeshan Qasim

2 Jiangsu Key Laboratory of Chemical Pollution Control and Resources Reuse, School of Environmental and Biological Engineering, Nanjing University of Science and Technology, Xiaolingwei 200, Nanjing, 210094 People’s Republic of China

Huaming Song

Muntasir murshed.

3 School of Business and Economics, North South University, Dhaka, 1229 Bangladesh

4 Department of Journalism, Media and Communications, Daffodil International University, Dhaka, Bangladesh

Haider Mahmood

5 Department of Finance, College of Business Administration, Prince Sattam Bin Abdulaziz University, 173, Alkharj, 11942 Saudi Arabia

Ijaz Younis

Associated data.

Data sources and relevant links are provided in the paper to access data.

Climate change is a long-lasting change in the weather arrays across tropics to polls. It is a global threat that has embarked on to put stress on various sectors. This study is aimed to conceptually engineer how climate variability is deteriorating the sustainability of diverse sectors worldwide. Specifically, the agricultural sector’s vulnerability is a globally concerning scenario, as sufficient production and food supplies are threatened due to irreversible weather fluctuations. In turn, it is challenging the global feeding patterns, particularly in countries with agriculture as an integral part of their economy and total productivity. Climate change has also put the integrity and survival of many species at stake due to shifts in optimum temperature ranges, thereby accelerating biodiversity loss by progressively changing the ecosystem structures. Climate variations increase the likelihood of particular food and waterborne and vector-borne diseases, and a recent example is a coronavirus pandemic. Climate change also accelerates the enigma of antimicrobial resistance, another threat to human health due to the increasing incidence of resistant pathogenic infections. Besides, the global tourism industry is devastated as climate change impacts unfavorable tourism spots. The methodology investigates hypothetical scenarios of climate variability and attempts to describe the quality of evidence to facilitate readers’ careful, critical engagement. Secondary data is used to identify sustainability issues such as environmental, social, and economic viability. To better understand the problem, gathered the information in this report from various media outlets, research agencies, policy papers, newspapers, and other sources. This review is a sectorial assessment of climate change mitigation and adaptation approaches worldwide in the aforementioned sectors and the associated economic costs. According to the findings, government involvement is necessary for the country’s long-term development through strict accountability of resources and regulations implemented in the past to generate cutting-edge climate policy. Therefore, mitigating the impacts of climate change must be of the utmost importance, and hence, this global threat requires global commitment to address its dreadful implications to ensure global sustenance.

Introduction

Worldwide observed and anticipated climatic changes for the twenty-first century and global warming are significant global changes that have been encountered during the past 65 years. Climate change (CC) is an inter-governmental complex challenge globally with its influence over various components of the ecological, environmental, socio-political, and socio-economic disciplines (Adger et al.  2005 ; Leal Filho et al.  2021 ; Feliciano et al.  2022 ). Climate change involves heightened temperatures across numerous worlds (Battisti and Naylor  2009 ; Schuurmans  2021 ; Weisheimer and Palmer  2005 ; Yadav et al.  2015 ). With the onset of the industrial revolution, the problem of earth climate was amplified manifold (Leppänen et al.  2014 ). It is reported that the immediate attention and due steps might increase the probability of overcoming its devastating impacts. It is not plausible to interpret the exact consequences of climate change (CC) on a sectoral basis (Izaguirre et al.  2021 ; Jurgilevich et al.  2017 ), which is evident by the emerging level of recognition plus the inclusion of climatic uncertainties at both local and national level of policymaking (Ayers et al.  2014 ).

Climate change is characterized based on the comprehensive long-haul temperature and precipitation trends and other components such as pressure and humidity level in the surrounding environment. Besides, the irregular weather patterns, retreating of global ice sheets, and the corresponding elevated sea level rise are among the most renowned international and domestic effects of climate change (Lipczynska-Kochany  2018 ; Michel et al.  2021 ; Murshed and Dao 2020 ). Before the industrial revolution, natural sources, including volcanoes, forest fires, and seismic activities, were regarded as the distinct sources of greenhouse gases (GHGs) such as CO 2 , CH 4 , N 2 O, and H 2 O into the atmosphere (Murshed et al. 2020 ; Hussain et al.  2020 ; Sovacool et al.  2021 ; Usman and Balsalobre-Lorente 2022 ; Murshed 2022 ). United Nations Framework Convention on Climate Change (UNFCCC) struck a major agreement to tackle climate change and accelerate and intensify the actions and investments required for a sustainable low-carbon future at Conference of the Parties (COP-21) in Paris on December 12, 2015. The Paris Agreement expands on the Convention by bringing all nations together for the first time in a single cause to undertake ambitious measures to prevent climate change and adapt to its impacts, with increased funding to assist developing countries in doing so. As so, it marks a turning point in the global climate fight. The core goal of the Paris Agreement is to improve the global response to the threat of climate change by keeping the global temperature rise this century well below 2 °C over pre-industrial levels and to pursue efforts to limit the temperature increase to 1.5° C (Sharma et al. 2020 ; Sharif et al. 2020 ; Chien et al. 2021 .

Furthermore, the agreement aspires to strengthen nations’ ability to deal with the effects of climate change and align financing flows with low GHG emissions and climate-resilient paths (Shahbaz et al. 2019 ; Anwar et al. 2021 ; Usman et al. 2022a ). To achieve these lofty goals, adequate financial resources must be mobilized and provided, as well as a new technology framework and expanded capacity building, allowing developing countries and the most vulnerable countries to act under their respective national objectives. The agreement also establishes a more transparent action and support mechanism. All Parties are required by the Paris Agreement to do their best through “nationally determined contributions” (NDCs) and to strengthen these efforts in the coming years (Balsalobre-Lorente et al. 2020 ). It includes obligations that all Parties regularly report on their emissions and implementation activities. A global stock-take will be conducted every five years to review collective progress toward the agreement’s goal and inform the Parties’ future individual actions. The Paris Agreement became available for signature on April 22, 2016, Earth Day, at the United Nations Headquarters in New York. On November 4, 2016, it went into effect 30 days after the so-called double threshold was met (ratification by 55 nations accounting for at least 55% of world emissions). More countries have ratified and continue to ratify the agreement since then, bringing 125 Parties in early 2017. To fully operationalize the Paris Agreement, a work program was initiated in Paris to define mechanisms, processes, and recommendations on a wide range of concerns (Murshed et al. 2021 ). Since 2016, Parties have collaborated in subsidiary bodies (APA, SBSTA, and SBI) and numerous formed entities. The Conference of the Parties functioning as the meeting of the Parties to the Paris Agreement (CMA) convened for the first time in November 2016 in Marrakesh in conjunction with COP22 and made its first two resolutions. The work plan is scheduled to be finished by 2018. Some mitigation and adaptation strategies to reduce the emission in the prospective of Paris agreement are following firstly, a long-term goal of keeping the increase in global average temperature to well below 2 °C above pre-industrial levels, secondly, to aim to limit the rise to 1.5 °C, since this would significantly reduce risks and the impacts of climate change, thirdly, on the need for global emissions to peak as soon as possible, recognizing that this will take longer for developing countries, lastly, to undertake rapid reductions after that under the best available science, to achieve a balance between emissions and removals in the second half of the century. On the other side, some adaptation strategies are; strengthening societies’ ability to deal with the effects of climate change and to continue & expand international assistance for developing nations’ adaptation.

However, anthropogenic activities are currently regarded as most accountable for CC (Murshed et al. 2022 ). Apart from the industrial revolution, other anthropogenic activities include excessive agricultural operations, which further involve the high use of fuel-based mechanization, burning of agricultural residues, burning fossil fuels, deforestation, national and domestic transportation sectors, etc. (Huang et al.  2016 ). Consequently, these anthropogenic activities lead to climatic catastrophes, damaging local and global infrastructure, human health, and total productivity. Energy consumption has mounted GHGs levels concerning warming temperatures as most of the energy production in developing countries comes from fossil fuels (Balsalobre-Lorente et al. 2022 ; Usman et al. 2022b ; Abbass et al. 2021a ; Ishikawa-Ishiwata and Furuya  2022 ).

This review aims to highlight the effects of climate change in a socio-scientific aspect by analyzing the existing literature on various sectorial pieces of evidence globally that influence the environment. Although this review provides a thorough examination of climate change and its severe affected sectors that pose a grave danger for global agriculture, biodiversity, health, economy, forestry, and tourism, and to purpose some practical prophylactic measures and mitigation strategies to be adapted as sound substitutes to survive from climate change (CC) impacts. The societal implications of irregular weather patterns and other effects of climate changes are discussed in detail. Some numerous sustainable mitigation measures and adaptation practices and techniques at the global level are discussed in this review with an in-depth focus on its economic, social, and environmental aspects. Methods of data collection section are included in the supplementary information.

Review methodology

Related study and its objectives.

Today, we live an ordinary life in the beautiful digital, globalized world where climate change has a decisive role. What happens in one country has a massive influence on geographically far apart countries, which points to the current crisis known as COVID-19 (Sarkar et al.  2021 ). The most dangerous disease like COVID-19 has affected the world’s climate changes and economic conditions (Abbass et al. 2022 ; Pirasteh-Anosheh et al.  2021 ). The purpose of the present study is to review the status of research on the subject, which is based on “Global Climate Change Impacts, adaptation, and sustainable mitigation measures” by systematically reviewing past published and unpublished research work. Furthermore, the current study seeks to comment on research on the same topic and suggest future research on the same topic. Specifically, the present study aims: The first one is, organize publications to make them easy and quick to find. Secondly, to explore issues in this area, propose an outline of research for future work. The third aim of the study is to synthesize the previous literature on climate change, various sectors, and their mitigation measurement. Lastly , classify the articles according to the different methods and procedures that have been adopted.

Review methodology for reviewers

This review-based article followed systematic literature review techniques that have proved the literature review as a rigorous framework (Benita  2021 ; Tranfield et al.  2003 ). Moreover, we illustrate in Fig.  1 the search method that we have started for this research. First, finalized the research theme to search literature (Cooper et al.  2018 ). Second, used numerous research databases to search related articles and download from the database (Web of Science, Google Scholar, Scopus Index Journals, Emerald, Elsevier Science Direct, Springer, and Sciverse). We focused on various articles, with research articles, feedback pieces, short notes, debates, and review articles published in scholarly journals. Reports used to search for multiple keywords such as “Climate Change,” “Mitigation and Adaptation,” “Department of Agriculture and Human Health,” “Department of Biodiversity and Forestry,” etc.; in summary, keyword list and full text have been made. Initially, the search for keywords yielded a large amount of literature.

Methodology search for finalized articles for investigations.

Source : constructed by authors

Since 2020, it has been impossible to review all the articles found; some restrictions have been set for the literature exhibition. The study searched 95 articles on a different database mentioned above based on the nature of the study. It excluded 40 irrelevant papers due to copied from a previous search after readings tiles, abstract and full pieces. The criteria for inclusion were: (i) articles focused on “Global Climate Change Impacts, adaptation, and sustainable mitigation measures,” and (ii) the search key terms related to study requirements. The complete procedure yielded 55 articles for our study. We repeat our search on the “Web of Science and Google Scholars” database to enhance the search results and check the referenced articles.

In this study, 55 articles are reviewed systematically and analyzed for research topics and other aspects, such as the methods, contexts, and theories used in these studies. Furthermore, this study analyzes closely related areas to provide unique research opportunities in the future. The study also discussed future direction opportunities and research questions by understanding the research findings climate changes and other affected sectors. The reviewed paper framework analysis process is outlined in Fig.  2 .

Framework of the analysis Process.

Natural disasters and climate change’s socio-economic consequences

Natural and environmental disasters can be highly variable from year to year; some years pass with very few deaths before a significant disaster event claims many lives (Symanski et al.  2021 ). Approximately 60,000 people globally died from natural disasters each year on average over the past decade (Ritchie and Roser  2014 ; Wiranata and Simbolon  2021 ). So, according to the report, around 0.1% of global deaths. Annual variability in the number and share of deaths from natural disasters in recent decades are shown in Fig.  3 . The number of fatalities can be meager—sometimes less than 10,000, and as few as 0.01% of all deaths. But shock events have a devastating impact: the 1983–1985 famine and drought in Ethiopia; the 2004 Indian Ocean earthquake and tsunami; Cyclone Nargis, which struck Myanmar in 2008; and the 2010 Port-au-Prince earthquake in Haiti and now recent example is COVID-19 pandemic (Erman et al.  2021 ). These events pushed global disaster deaths to over 200,000—more than 0.4% of deaths in these years. Low-frequency, high-impact events such as earthquakes and tsunamis are not preventable, but such high losses of human life are. Historical evidence shows that earlier disaster detection, more robust infrastructure, emergency preparedness, and response programmers have substantially reduced disaster deaths worldwide. Low-income is also the most vulnerable to disasters; improving living conditions, facilities, and response services in these areas would be critical in reducing natural disaster deaths in the coming decades.

Global deaths from natural disasters, 1978 to 2020.

Source EMDAT ( 2020 )

The interior regions of the continent are likely to be impacted by rising temperatures (Dimri et al.  2018 ; Goes et al.  2020 ; Mannig et al.  2018 ; Schuurmans  2021 ). Weather patterns change due to the shortage of natural resources (water), increase in glacier melting, and rising mercury are likely to cause extinction to many planted species (Gampe et al.  2016 ; Mihiretu et al.  2021 ; Shaffril et al.  2018 ).On the other hand, the coastal ecosystem is on the verge of devastation (Perera et al.  2018 ; Phillips  2018 ). The temperature rises, insect disease outbreaks, health-related problems, and seasonal and lifestyle changes are persistent, with a strong probability of these patterns continuing in the future (Abbass et al. 2021c ; Hussain et al.  2018 ). At the global level, a shortage of good infrastructure and insufficient adaptive capacity are hammering the most (IPCC  2013 ). In addition to the above concerns, a lack of environmental education and knowledge, outdated consumer behavior, a scarcity of incentives, a lack of legislation, and the government’s lack of commitment to climate change contribute to the general public’s concerns. By 2050, a 2 to 3% rise in mercury and a drastic shift in rainfall patterns may have serious consequences (Huang et al. 2022 ; Gorst et al.  2018 ). Natural and environmental calamities caused huge losses globally, such as decreased agriculture outputs, rehabilitation of the system, and rebuilding necessary technologies (Ali and Erenstein  2017 ; Ramankutty et al.  2018 ; Yu et al.  2021 ) (Table ​ (Table1). 1 ). Furthermore, in the last 3 or 4 years, the world has been plagued by smog-related eye and skin diseases, as well as a rise in road accidents due to poor visibility.

Main natural danger statistics for 1985–2020 at the global level

Source: EM-DAT ( 2020 )

Climate change and agriculture

Global agriculture is the ultimate sector responsible for 30–40% of all greenhouse emissions, which makes it a leading industry predominantly contributing to climate warming and significantly impacted by it (Grieg; Mishra et al.  2021 ; Ortiz et al.  2021 ; Thornton and Lipper  2014 ). Numerous agro-environmental and climatic factors that have a dominant influence on agriculture productivity (Pautasso et al.  2012 ) are significantly impacted in response to precipitation extremes including floods, forest fires, and droughts (Huang  2004 ). Besides, the immense dependency on exhaustible resources also fuels the fire and leads global agriculture to become prone to devastation. Godfray et al. ( 2010 ) mentioned that decline in agriculture challenges the farmer’s quality of life and thus a significant factor to poverty as the food and water supplies are critically impacted by CC (Ortiz et al.  2021 ; Rosenzweig et al.  2014 ). As an essential part of the economic systems, especially in developing countries, agricultural systems affect the overall economy and potentially the well-being of households (Schlenker and Roberts  2009 ). According to the report published by the Intergovernmental Panel on Climate Change (IPCC), atmospheric concentrations of greenhouse gases, i.e., CH 4, CO 2 , and N 2 O, are increased in the air to extraordinary levels over the last few centuries (Usman and Makhdum 2021 ; Stocker et al.  2013 ). Climate change is the composite outcome of two different factors. The first is the natural causes, and the second is the anthropogenic actions (Karami 2012 ). It is also forecasted that the world may experience a typical rise in temperature stretching from 1 to 3.7 °C at the end of this century (Pachauri et al. 2014 ). The world’s crop production is also highly vulnerable to these global temperature-changing trends as raised temperatures will pose severe negative impacts on crop growth (Reidsma et al. 2009 ). Some of the recent modeling about the fate of global agriculture is briefly described below.

Decline in cereal productivity

Crop productivity will also be affected dramatically in the next few decades due to variations in integral abiotic factors such as temperature, solar radiation, precipitation, and CO 2 . These all factors are included in various regulatory instruments like progress and growth, weather-tempted changes, pest invasions (Cammell and Knight 1992 ), accompanying disease snags (Fand et al. 2012 ), water supplies (Panda et al. 2003 ), high prices of agro-products in world’s agriculture industry, and preeminent quantity of fertilizer consumption. Lobell and field ( 2007 ) claimed that from 1962 to 2002, wheat crop output had condensed significantly due to rising temperatures. Therefore, during 1980–2011, the common wheat productivity trends endorsed extreme temperature events confirmed by Gourdji et al. ( 2013 ) around South Asia, South America, and Central Asia. Various other studies (Asseng, Cao, Zhang, and Ludwig 2009 ; Asseng et al. 2013 ; García et al. 2015 ; Ortiz et al. 2021 ) also proved that wheat output is negatively affected by the rising temperatures and also caused adverse effects on biomass productivity (Calderini et al. 1999 ; Sadras and Slafer 2012 ). Hereafter, the rice crop is also influenced by the high temperatures at night. These difficulties will worsen because the temperature will be rising further in the future owing to CC (Tebaldi et al. 2006 ). Another research conducted in China revealed that a 4.6% of rice production per 1 °C has happened connected with the advancement in night temperatures (Tao et al. 2006 ). Moreover, the average night temperature growth also affected rice indicia cultivar’s output pragmatically during 25 years in the Philippines (Peng et al. 2004 ). It is anticipated that the increase in world average temperature will also cause a substantial reduction in yield (Hatfield et al. 2011 ; Lobell and Gourdji 2012 ). In the southern hemisphere, Parry et al. ( 2007 ) noted a rise of 1–4 °C in average daily temperatures at the end of spring season unti the middle of summers, and this raised temperature reduced crop output by cutting down the time length for phenophases eventually reduce the yield (Hatfield and Prueger 2015 ; R. Ortiz 2008 ). Also, world climate models have recommended that humid and subtropical regions expect to be plentiful prey to the upcoming heat strokes (Battisti and Naylor 2009 ). Grain production is the amalgamation of two constituents: the average weight and the grain output/m 2 , however, in crop production. Crop output is mainly accredited to the grain quantity (Araus et al. 2008 ; Gambín and Borrás 2010 ). In the times of grain set, yield resources are mainly strewn between hitherto defined components, i.e., grain usual weight and grain output, which presents a trade-off between them (Gambín and Borrás 2010 ) beside disparities in per grain integration (B. L. Gambín et al. 2006 ). In addition to this, the maize crop is also susceptible to raised temperatures, principally in the flowering stage (Edreira and Otegui 2013 ). In reality, the lower grain number is associated with insufficient acclimatization due to intense photosynthesis and higher respiration and the high-temperature effect on the reproduction phenomena (Edreira and Otegui 2013 ). During the flowering phase, maize visible to heat (30–36 °C) seemed less anthesis-silking intermissions (Edreira et al. 2011 ). Another research by Dupuis and Dumas ( 1990 ) proved that a drop in spikelet when directly visible to high temperatures above 35 °C in vitro pollination. Abnormalities in kernel number claimed by Vega et al. ( 2001 ) is related to conceded plant development during a flowering phase that is linked with the active ear growth phase and categorized as a critical phase for approximation of kernel number during silking (Otegui and Bonhomme 1998 ).

The retort of rice output to high temperature presents disparities in flowering patterns, and seed set lessens and lessens grain weight (Qasim et al. 2020 ; Qasim, Hammad, Maqsood, Tariq, & Chawla). During the daytime, heat directly impacts flowers which lessens the thesis period and quickens the earlier peak flowering (Tao et al. 2006 ). Antagonistic effect of higher daytime temperature d on pollen sprouting proposed seed set decay, whereas, seed set was lengthily reduced than could be explicated by pollen growing at high temperatures 40◦C (Matsui et al. 2001 ).

The decline in wheat output is linked with higher temperatures, confirmed in numerous studies (Semenov 2009 ; Stone and Nicolas 1994 ). High temperatures fast-track the arrangements of plant expansion (Blum et al. 2001 ), diminution photosynthetic process (Salvucci and Crafts‐Brandner 2004 ), and also considerably affect the reproductive operations (Farooq et al. 2011 ).

The destructive impacts of CC induced weather extremes to deteriorate the integrity of crops (Chaudhary et al. 2011 ), e.g., Spartan cold and extreme fog cause falling and discoloration of betel leaves (Rosenzweig et al. 2001 ), giving them a somehow reddish appearance, squeezing of lemon leaves (Pautasso et al. 2012 ), as well as root rot of pineapple, have reported (Vedwan and Rhoades 2001 ). Henceforth, in tackling the disruptive effects of CC, several short-term and long-term management approaches are the crucial need of time (Fig.  4 ). Moreover, various studies (Chaudhary et al. 2011 ; Patz et al. 2005 ; Pautasso et al. 2012 ) have demonstrated adapting trends such as ameliorating crop diversity can yield better adaptability towards CC.

Schematic description of potential impacts of climate change on the agriculture sector and the appropriate mitigation and adaptation measures to overcome its impact.

Climate change impacts on biodiversity

Global biodiversity is among the severe victims of CC because it is the fastest emerging cause of species loss. Studies demonstrated that the massive scale species dynamics are considerably associated with diverse climatic events (Abraham and Chain 1988 ; Manes et al. 2021 ; A. M. D. Ortiz et al. 2021 ). Both the pace and magnitude of CC are altering the compatible habitat ranges for living entities of marine, freshwater, and terrestrial regions. Alterations in general climate regimes influence the integrity of ecosystems in numerous ways, such as variation in the relative abundance of species, range shifts, changes in activity timing, and microhabitat use (Bates et al. 2014 ). The geographic distribution of any species often depends upon its ability to tolerate environmental stresses, biological interactions, and dispersal constraints. Hence, instead of the CC, the local species must only accept, adapt, move, or face extinction (Berg et al. 2010 ). So, the best performer species have a better survival capacity for adjusting to new ecosystems or a decreased perseverance to survive where they are already situated (Bates et al. 2014 ). An important aspect here is the inadequate habitat connectivity and access to microclimates, also crucial in raising the exposure to climate warming and extreme heatwave episodes. For example, the carbon sequestration rates are undergoing fluctuations due to climate-driven expansion in the range of global mangroves (Cavanaugh et al. 2014 ).

Similarly, the loss of kelp-forest ecosystems in various regions and its occupancy by the seaweed turfs has set the track for elevated herbivory by the high influx of tropical fish populations. Not only this, the increased water temperatures have exacerbated the conditions far away from the physiological tolerance level of the kelp communities (Vergés et al. 2016 ; Wernberg et al. 2016 ). Another pertinent danger is the devastation of keystone species, which even has more pervasive effects on the entire communities in that habitat (Zarnetske et al. 2012 ). It is particularly important as CC does not specify specific populations or communities. Eventually, this CC-induced redistribution of species may deteriorate carbon storage and the net ecosystem productivity (Weed et al. 2013 ). Among the typical disruptions, the prominent ones include impacts on marine and terrestrial productivity, marine community assembly, and the extended invasion of toxic cyanobacteria bloom (Fossheim et al. 2015 ).

The CC-impacted species extinction is widely reported in the literature (Beesley et al. 2019 ; Urban 2015 ), and the predictions of demise until the twenty-first century are dreadful (Abbass et al. 2019 ; Pereira et al. 2013 ). In a few cases, northward shifting of species may not be formidable as it allows mountain-dwelling species to find optimum climates. However, the migrant species may be trapped in isolated and incompatible habitats due to losing topography and range (Dullinger et al. 2012 ). For example, a study indicated that the American pika has been extirpated or intensely diminished in some regions, primarily attributed to the CC-impacted extinction or at least local extirpation (Stewart et al. 2015 ). Besides, the anticipation of persistent responses to the impacts of CC often requires data records of several decades to rigorously analyze the critical pre and post CC patterns at species and ecosystem levels (Manes et al. 2021 ; Testa et al. 2018 ).

Nonetheless, the availability of such long-term data records is rare; hence, attempts are needed to focus on these profound aspects. Biodiversity is also vulnerable to the other associated impacts of CC, such as rising temperatures, droughts, and certain invasive pest species. For instance, a study revealed the changes in the composition of plankton communities attributed to rising temperatures. Henceforth, alterations in such aquatic producer communities, i.e., diatoms and calcareous plants, can ultimately lead to variation in the recycling of biological carbon. Moreover, such changes are characterized as a potential contributor to CO 2 differences between the Pleistocene glacial and interglacial periods (Kohfeld et al. 2005 ).

Climate change implications on human health

It is an understood corporality that human health is a significant victim of CC (Costello et al. 2009 ). According to the WHO, CC might be responsible for 250,000 additional deaths per year during 2030–2050 (Watts et al. 2015 ). These deaths are attributed to extreme weather-induced mortality and morbidity and the global expansion of vector-borne diseases (Lemery et al. 2021; Yang and Usman 2021 ; Meierrieks 2021 ; UNEP 2017 ). Here, some of the emerging health issues pertinent to this global problem are briefly described.

Climate change and antimicrobial resistance with corresponding economic costs

Antimicrobial resistance (AMR) is an up-surging complex global health challenge (Garner et al. 2019 ; Lemery et al. 2021 ). Health professionals across the globe are extremely worried due to this phenomenon that has critical potential to reverse almost all the progress that has been achieved so far in the health discipline (Gosling and Arnell 2016 ). A massive amount of antibiotics is produced by many pharmaceutical industries worldwide, and the pathogenic microorganisms are gradually developing resistance to them, which can be comprehended how strongly this aspect can shake the foundations of national and global economies (UNEP 2017 ). This statement is supported by the fact that AMR is not developing in a particular region or country. Instead, it is flourishing in every continent of the world (WHO 2018 ). This plague is heavily pushing humanity to the post-antibiotic era, in which currently antibiotic-susceptible pathogens will once again lead to certain endemics and pandemics after being resistant(WHO 2018 ). Undesirably, if this statement would become a factuality, there might emerge certain risks in undertaking sophisticated interventions such as chemotherapy, joint replacement cases, and organ transplantation (Su et al. 2018 ). Presently, the amplification of drug resistance cases has made common illnesses like pneumonia, post-surgical infections, HIV/AIDS, tuberculosis, malaria, etc., too difficult and costly to be treated or cure well (WHO 2018 ). From a simple example, it can be assumed how easily antibiotic-resistant strains can be transmitted from one person to another and ultimately travel across the boundaries (Berendonk et al. 2015 ). Talking about the second- and third-generation classes of antibiotics, e.g., most renowned generations of cephalosporin antibiotics that are more expensive, broad-spectrum, more toxic, and usually require more extended periods whenever prescribed to patients (Lemery et al. 2021 ; Pärnänen et al. 2019 ). This scenario has also revealed that the abundance of resistant strains of pathogens was also higher in the Southern part (WHO 2018 ). As southern parts are generally warmer than their counterparts, it is evident from this example how CC-induced global warming can augment the spread of antibiotic-resistant strains within the biosphere, eventually putting additional economic burden in the face of developing new and costlier antibiotics. The ARG exchange to susceptible bacteria through one of the potential mechanisms, transformation, transduction, and conjugation; Selection pressure can be caused by certain antibiotics, metals or pesticides, etc., as shown in Fig.  5 .

A typical interaction between the susceptible and resistant strains.

Source: Elsayed et al. ( 2021 ); Karkman et al. ( 2018 )

Certain studies highlighted that conventional urban wastewater treatment plants are typical hotspots where most bacterial strains exchange genetic material through horizontal gene transfer (Fig.  5 ). Although at present, the extent of risks associated with the antibiotic resistance found in wastewater is complicated; environmental scientists and engineers have particular concerns about the potential impacts of these antibiotic resistance genes on human health (Ashbolt 2015 ). At most undesirable and worst case, these antibiotic-resistant genes containing bacteria can make their way to enter into the environment (Pruden et al. 2013 ), irrigation water used for crops and public water supplies and ultimately become a part of food chains and food webs (Ma et al. 2019 ; D. Wu et al. 2019 ). This problem has been reported manifold in several countries (Hendriksen et al. 2019 ), where wastewater as a means of irrigated water is quite common.

Climate change and vector borne-diseases

Temperature is a fundamental factor for the sustenance of living entities regardless of an ecosystem. So, a specific living being, especially a pathogen, requires a sophisticated temperature range to exist on earth. The second essential component of CC is precipitation, which also impacts numerous infectious agents’ transport and dissemination patterns. Global rising temperature is a significant cause of many species extinction. On the one hand, this changing environmental temperature may be causing species extinction, and on the other, this warming temperature might favor the thriving of some new organisms. Here, it was evident that some pathogens may also upraise once non-evident or reported (Patz et al. 2000 ). This concept can be exemplified through certain pathogenic strains of microorganisms that how the likelihood of various diseases increases in response to climate warming-induced environmental changes (Table ​ (Table2 2 ).

Examples of how various environmental changes affect various infectious diseases in humans

Source: Aron and Patz ( 2001 )

A recent example is an outburst of coronavirus (COVID-19) in the Republic of China, causing pneumonia and severe acute respiratory complications (Cui et al. 2021 ; Song et al. 2021 ). The large family of viruses is harbored in numerous animals, bats, and snakes in particular (livescience.com) with the subsequent transfer into human beings. Hence, it is worth noting that the thriving of numerous vectors involved in spreading various diseases is influenced by Climate change (Ogden 2018 ; Santos et al. 2021 ).

Psychological impacts of climate change

Climate change (CC) is responsible for the rapid dissemination and exaggeration of certain epidemics and pandemics. In addition to the vast apparent impacts of climate change on health, forestry, agriculture, etc., it may also have psychological implications on vulnerable societies. It can be exemplified through the recent outburst of (COVID-19) in various countries around the world (Pal 2021 ). Besides, the victims of this viral infection have made healthy beings scarier and terrified. In the wake of such epidemics, people with common colds or fever are also frightened and must pass specific regulatory protocols. Living in such situations continuously terrifies the public and makes the stress familiar, which eventually makes them psychologically weak (npr.org).

CC boosts the extent of anxiety, distress, and other issues in public, pushing them to develop various mental-related problems. Besides, frequent exposure to extreme climatic catastrophes such as geological disasters also imprints post-traumatic disorder, and their ubiquitous occurrence paves the way to developing chronic psychological dysfunction. Moreover, repetitive listening from media also causes an increase in the person’s stress level (Association 2020 ). Similarly, communities living in flood-prone areas constantly live in extreme fear of drowning and die by floods. In addition to human lives, the flood-induced destruction of physical infrastructure is a specific reason for putting pressure on these communities (Ogden 2018 ). For instance, Ogden ( 2018 ) comprehensively denoted that Katrina’s Hurricane augmented the mental health issues in the victim communities.

Climate change impacts on the forestry sector

Forests are the global regulators of the world’s climate (FAO 2018 ) and have an indispensable role in regulating global carbon and nitrogen cycles (Rehman et al. 2021 ; Reichstein and Carvalhais 2019 ). Hence, disturbances in forest ecology affect the micro and macro-climates (Ellison et al. 2017 ). Climate warming, in return, has profound impacts on the growth and productivity of transboundary forests by influencing the temperature and precipitation patterns, etc. As CC induces specific changes in the typical structure and functions of ecosystems (Zhang et al. 2017 ) as well impacts forest health, climate change also has several devastating consequences such as forest fires, droughts, pest outbreaks (EPA 2018 ), and last but not the least is the livelihoods of forest-dependent communities. The rising frequency and intensity of another CC product, i.e., droughts, pose plenty of challenges to the well-being of global forests (Diffenbaugh et al. 2017 ), which is further projected to increase soon (Hartmann et al. 2018 ; Lehner et al. 2017 ; Rehman et al. 2021 ). Hence, CC induces storms, with more significant impacts also put extra pressure on the survival of the global forests (Martínez-Alvarado et al. 2018 ), significantly since their influences are augmented during higher winter precipitations with corresponding wetter soils causing weak root anchorage of trees (Brázdil et al. 2018 ). Surging temperature regimes causes alterations in usual precipitation patterns, which is a significant hurdle for the survival of temperate forests (Allen et al. 2010 ; Flannigan et al. 2013 ), letting them encounter severe stress and disturbances which adversely affects the local tree species (Hubbart et al. 2016 ; Millar and Stephenson 2015 ; Rehman et al. 2021 ).

Climate change impacts on forest-dependent communities

Forests are the fundamental livelihood resource for about 1.6 billion people worldwide; out of them, 350 million are distinguished with relatively higher reliance (Bank 2008 ). Agro-forestry-dependent communities comprise 1.2 billion, and 60 million indigenous people solely rely on forests and their products to sustain their lives (Sunderlin et al. 2005 ). For example, in the entire African continent, more than 2/3rd of inhabitants depend on forest resources and woodlands for their alimonies, e.g., food, fuelwood and grazing (Wasiq and Ahmad 2004 ). The livings of these people are more intensely affected by the climatic disruptions making their lives harder (Brown et al. 2014 ). On the one hand, forest communities are incredibly vulnerable to CC due to their livelihoods, cultural and spiritual ties as well as socio-ecological connections, and on the other, they are not familiar with the term “climate change.” (Rahman and Alam 2016 ). Among the destructive impacts of temperature and rainfall, disruption of the agroforestry crops with resultant downscale growth and yield (Macchi et al. 2008 ). Cruz ( 2015 ) ascribed that forest-dependent smallholder farmers in the Philippines face the enigma of delayed fruiting, more severe damages by insect and pest incidences due to unfavorable temperature regimes, and changed rainfall patterns.

Among these series of challenges to forest communities, their well-being is also distinctly vulnerable to CC. Though the detailed climate change impacts on human health have been comprehensively mentioned in the previous section, some studies have listed a few more devastating effects on the prosperity of forest-dependent communities. For instance, the Himalayan people have been experiencing frequent skin-borne diseases such as malaria and other skin diseases due to increasing mosquitoes, wild boar as well, and new wasps species, particularly in higher altitudes that were almost non-existent before last 5–10 years (Xu et al. 2008 ). Similarly, people living at high altitudes in Bangladesh have experienced frequent mosquito-borne calamities (Fardous; Sharma 2012 ). In addition, the pace of other waterborne diseases such as infectious diarrhea, cholera, pathogenic induced abdominal complications and dengue has also been boosted in other distinguished regions of Bangladesh (Cell 2009 ; Gunter et al. 2008 ).

Pest outbreak

Upscaling hotter climate may positively affect the mobile organisms with shorter generation times because they can scurry from harsh conditions than the immobile species (Fettig et al. 2013 ; Schoene and Bernier 2012 ) and are also relatively more capable of adapting to new environments (Jactel et al. 2019 ). It reveals that insects adapt quickly to global warming due to their mobility advantages. Due to past outbreaks, the trees (forests) are relatively more susceptible victims (Kurz et al. 2008 ). Before CC, the influence of factors mentioned earlier, i.e., droughts and storms, was existent and made the forests susceptible to insect pest interventions; however, the global forests remain steadfast, assiduous, and green (Jactel et al. 2019 ). The typical reasons could be the insect herbivores were regulated by several tree defenses and pressures of predation (Wilkinson and Sherratt 2016 ). As climate greatly influences these phenomena, the global forests cannot be so sedulous against such challenges (Jactel et al. 2019 ). Table ​ Table3 3 demonstrates some of the particular considerations with practical examples that are essential while mitigating the impacts of CC in the forestry sector.

Essential considerations while mitigating the climate change impacts on the forestry sector

Source : Fischer ( 2019 )

Climate change impacts on tourism

Tourism is a commercial activity that has roots in multi-dimensions and an efficient tool with adequate job generation potential, revenue creation, earning of spectacular foreign exchange, enhancement in cross-cultural promulgation and cooperation, a business tool for entrepreneurs and eventually for the country’s national development (Arshad et al. 2018 ; Scott 2021 ). Among a plethora of other disciplines, the tourism industry is also a distinct victim of climate warming (Gössling et al. 2012 ; Hall et al. 2015 ) as the climate is among the essential resources that enable tourism in particular regions as most preferred locations. Different places at different times of the year attract tourists both within and across the countries depending upon the feasibility and compatibility of particular weather patterns. Hence, the massive variations in these weather patterns resulting from CC will eventually lead to monumental challenges to the local economy in that specific area’s particular and national economy (Bujosa et al. 2015 ). For instance, the Intergovernmental Panel on Climate Change (IPCC) report demonstrated that the global tourism industry had faced a considerable decline in the duration of ski season, including the loss of some ski areas and the dramatic shifts in tourist destinations’ climate warming.

Furthermore, different studies (Neuvonen et al. 2015 ; Scott et al. 2004 ) indicated that various currently perfect tourist spots, e.g., coastal areas, splendid islands, and ski resorts, will suffer consequences of CC. It is also worth noting that the quality and potential of administrative management potential to cope with the influence of CC on the tourism industry is of crucial significance, which renders specific strengths of resiliency to numerous destinations to withstand against it (Füssel and Hildén 2014 ). Similarly, in the partial or complete absence of adequate socio-economic and socio-political capital, the high-demanding tourist sites scurry towards the verge of vulnerability. The susceptibility of tourism is based on different components such as the extent of exposure, sensitivity, life-supporting sectors, and capacity assessment factors (Füssel and Hildén 2014 ). It is obvious corporality that sectors such as health, food, ecosystems, human habitat, infrastructure, water availability, and the accessibility of a particular region are prone to CC. Henceforth, the sensitivity of these critical sectors to CC and, in return, the adaptive measures are a hallmark in determining the composite vulnerability of climate warming (Ionescu et al. 2009 ).

Moreover, the dependence on imported food items, poor hygienic conditions, and inadequate health professionals are dominant aspects affecting the local terrestrial and aquatic biodiversity. Meanwhile, the greater dependency on ecosystem services and its products also makes a destination more fragile to become a prey of CC (Rizvi et al. 2015 ). Some significant non-climatic factors are important indicators of a particular ecosystem’s typical health and functioning, e.g., resource richness and abundance portray the picture of ecosystem stability. Similarly, the species abundance is also a productive tool that ensures that the ecosystem has a higher buffering capacity, which is terrific in terms of resiliency (Roscher et al. 2013 ).

Climate change impacts on the economic sector

Climate plays a significant role in overall productivity and economic growth. Due to its increasingly global existence and its effect on economic growth, CC has become one of the major concerns of both local and international environmental policymakers (Ferreira et al. 2020 ; Gleditsch 2021 ; Abbass et al. 2021b ; Lamperti et al. 2021 ). The adverse effects of CC on the overall productivity factor of the agricultural sector are therefore significant for understanding the creation of local adaptation policies and the composition of productive climate policy contracts. Previous studies on CC in the world have already forecasted its effects on the agricultural sector. Researchers have found that global CC will impact the agricultural sector in different world regions. The study of the impacts of CC on various agrarian activities in other demographic areas and the development of relative strategies to respond to effects has become a focal point for researchers (Chandioet al. 2020 ; Gleditsch 2021 ; Mosavi et al. 2020 ).

With the rapid growth of global warming since the 1980s, the temperature has started increasing globally, which resulted in the incredible transformation of rain and evaporation in the countries. The agricultural development of many countries has been reliant, delicate, and susceptible to CC for a long time, and it is on the development of agriculture total factor productivity (ATFP) influence different crops and yields of farmers (Alhassan 2021 ; Wu  2020 ).

Food security and natural disasters are increasing rapidly in the world. Several major climatic/natural disasters have impacted local crop production in the countries concerned. The effects of these natural disasters have been poorly controlled by the development of the economies and populations and may affect human life as well. One example is China, which is among the world’s most affected countries, vulnerable to natural disasters due to its large population, harsh environmental conditions, rapid CC, low environmental stability, and disaster power. According to the January 2016 statistical survey, China experienced an economic loss of 298.3 billion Yuan, and about 137 million Chinese people were severely affected by various natural disasters (Xie et al. 2018 ).

Mitigation and adaptation strategies of climate changes

Adaptation and mitigation are the crucial factors to address the response to CC (Jahanzad et al. 2020 ). Researchers define mitigation on climate changes, and on the other hand, adaptation directly impacts climate changes like floods. To some extent, mitigation reduces or moderates greenhouse gas emission, and it becomes a critical issue both economically and environmentally (Botzen et al. 2021 ; Jahanzad et al. 2020 ; Kongsager 2018 ; Smit et al. 2000 ; Vale et al. 2021 ; Usman et al. 2021 ; Verheyen 2005 ).

Researchers have deep concern about the adaptation and mitigation methodologies in sectoral and geographical contexts. Agriculture, industry, forestry, transport, and land use are the main sectors to adapt and mitigate policies(Kärkkäinen et al. 2020 ; Waheed et al. 2021 ). Adaptation and mitigation require particular concern both at the national and international levels. The world has faced a significant problem of climate change in the last decades, and adaptation to these effects is compulsory for economic and social development. To adapt and mitigate against CC, one should develop policies and strategies at the international level (Hussain et al. 2020 ). Figure  6 depicts the list of current studies on sectoral impacts of CC with adaptation and mitigation measures globally.

Sectoral impacts of climate change with adaptation and mitigation measures.

Conclusion and future perspectives

Specific socio-agricultural, socio-economic, and physical systems are the cornerstone of psychological well-being, and the alteration in these systems by CC will have disastrous impacts. Climate variability, alongside other anthropogenic and natural stressors, influences human and environmental health sustainability. Food security is another concerning scenario that may lead to compromised food quality, higher food prices, and inadequate food distribution systems. Global forests are challenged by different climatic factors such as storms, droughts, flash floods, and intense precipitation. On the other hand, their anthropogenic wiping is aggrandizing their existence. Undoubtedly, the vulnerability scale of the world’s regions differs; however, appropriate mitigation and adaptation measures can aid the decision-making bodies in developing effective policies to tackle its impacts. Presently, modern life on earth has tailored to consistent climatic patterns, and accordingly, adapting to such considerable variations is of paramount importance. Because the faster changes in climate will make it harder to survive and adjust, this globally-raising enigma calls for immediate attention at every scale ranging from elementary community level to international level. Still, much effort, research, and dedication are required, which is the most critical time. Some policy implications can help us to mitigate the consequences of climate change, especially the most affected sectors like the agriculture sector;

Warming might lengthen the season in frost-prone growing regions (temperate and arctic zones), allowing for longer-maturing seasonal cultivars with better yields (Pfadenhauer 2020 ; Bonacci 2019 ). Extending the planting season may allow additional crops each year; when warming leads to frequent warmer months highs over critical thresholds, a split season with a brief summer fallow may be conceivable for short-period crops such as wheat barley, cereals, and many other vegetable crops. The capacity to prolong the planting season in tropical and subtropical places where the harvest season is constrained by precipitation or agriculture farming occurs after the year may be more limited and dependent on how precipitation patterns vary (Wu et al. 2017 ).

The genetic component is comprehensive for many yields, but it is restricted like kiwi fruit for a few. Ali et al. ( 2017 ) investigated how new crops will react to climatic changes (also stated in Mall et al. 2017 ). Hot temperature, drought, insect resistance; salt tolerance; and overall crop production and product quality increases would all be advantageous (Akkari 2016 ). Genetic mapping and engineering can introduce a greater spectrum of features. The adoption of genetically altered cultivars has been slowed, particularly in the early forecasts owing to the complexity in ensuring features are expediently expressed throughout the entire plant, customer concerns, economic profitability, and regulatory impediments (Wirehn 2018 ; Davidson et al. 2016 ).

To get the full benefit of the CO 2 would certainly require additional nitrogen and other fertilizers. Nitrogen not consumed by the plants may be excreted into groundwater, discharged into water surface, or emitted from the land, soil nitrous oxide when large doses of fertilizer are sprayed. Increased nitrogen levels in groundwater sources have been related to human chronic illnesses and impact marine ecosystems. Cultivation, grain drying, and other field activities have all been examined in depth in the studies (Barua et al. 2018 ).

• The technological and socio-economic adaptation

The policy consequence of the causative conclusion is that as a source of alternative energy, biofuel production is one of the routes that explain oil price volatility separate from international macroeconomic factors. Even though biofuel production has just begun in a few sample nations, there is still a tremendous worldwide need for feedstock to satisfy industrial expansion in China and the USA, which explains the food price relationship to the global oil price. Essentially, oil-exporting countries may create incentives in their economies to increase food production. It may accomplish by giving farmers financing, seedlings, fertilizers, and farming equipment. Because of the declining global oil price and, as a result, their earnings from oil export, oil-producing nations may be unable to subsidize food imports even in the near term. As a result, these countries can boost the agricultural value chain for export. It may be accomplished through R&D and adding value to their food products to increase income by correcting exchange rate misalignment and adverse trade terms. These nations may also diversify their economies away from oil, as dependence on oil exports alone is no longer economically viable given the extreme volatility of global oil prices. Finally, resource-rich and oil-exporting countries can convert to non-food renewable energy sources such as solar, hydro, coal, wind, wave, and tidal energy. By doing so, both world food and oil supplies would be maintained rather than harmed.

IRENA’s modeling work shows that, if a comprehensive policy framework is in place, efforts toward decarbonizing the energy future will benefit economic activity, jobs (outweighing losses in the fossil fuel industry), and welfare. Countries with weak domestic supply chains and a large reliance on fossil fuel income, in particular, must undertake structural reforms to capitalize on the opportunities inherent in the energy transition. Governments continue to give major policy assistance to extract fossil fuels, including tax incentives, financing, direct infrastructure expenditures, exemptions from environmental regulations, and other measures. The majority of major oil and gas producing countries intend to increase output. Some countries intend to cut coal output, while others plan to maintain or expand it. While some nations are beginning to explore and execute policies aimed at a just and equitable transition away from fossil fuel production, these efforts have yet to impact major producing countries’ plans and goals. Verifiable and comparable data on fossil fuel output and assistance from governments and industries are critical to closing the production gap. Governments could increase openness by declaring their production intentions in their climate obligations under the Paris Agreement.

It is firmly believed that achieving the Paris Agreement commitments is doubtlful without undergoing renewable energy transition across the globe (Murshed 2020 ; Zhao et al. 2022 ). Policy instruments play the most important role in determining the degree of investment in renewable energy technology. This study examines the efficacy of various policy strategies in the renewable energy industry of multiple nations. Although its impact is more visible in established renewable energy markets, a renewable portfolio standard is also a useful policy instrument. The cost of producing renewable energy is still greater than other traditional energy sources. Furthermore, government incentives in the R&D sector can foster innovation in this field, resulting in cost reductions in the renewable energy industry. These nations may export their technologies and share their policy experiences by forming networks among their renewable energy-focused organizations. All policy measures aim to reduce production costs while increasing the proportion of renewables to a country’s energy system. Meanwhile, long-term contracts with renewable energy providers, government commitment and control, and the establishment of long-term goals can assist developing nations in deploying renewable energy technology in their energy sector.

Author contribution

KA: Writing the original manuscript, data collection, data analysis, Study design, Formal analysis, Visualization, Revised draft, Writing-review, and editing. MZQ: Writing the original manuscript, data collection, data analysis, Writing-review, and editing. HS: Contribution to the contextualization of the theme, Conceptualization, Validation, Supervision, literature review, Revised drapt, and writing review and editing. MM: Writing review and editing, compiling the literature review, language editing. HM: Writing review and editing, compiling the literature review, language editing. IY: Contribution to the contextualization of the theme, literature review, and writing review and editing.

Availability of data and material

Declarations.

Not applicable.

The authors declare no competing interests.

Publisher's Note

Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Contributor Information

Kashif Abbass, Email: nc.ude.tsujn@ssabbafihsak .

Muhammad Zeeshan Qasim, Email: moc.kooltuo@888misaqnahseez .

Huaming Song, Email: nc.ude.tsujn@gnimauh .

Muntasir Murshed, Email: [email protected] .

Haider Mahmood, Email: moc.liamtoh@doomhamrediah .

Ijaz Younis, Email: nc.ude.tsujn@sinuoyzaji .

• Abbass K, Begum H, Alam ASA, Awang AH, Abdelsalam MK, Egdair IMM, Wahid R (2022) Fresh Insight through a Keynesian Theory Approach to Investigate the Economic Impact of the COVID-19 Pandemic in Pakistan. Sustain 14(3):1054
• Abbass K, Niazi AAK, Qazi TF, Basit A, Song H (2021a) The aftermath of COVID-19 pandemic period: barriers in implementation of social distancing at workplace. Library Hi Tech
• Abbass K, Song H, Khan F, Begum H, Asif M (2021b) Fresh insight through the VAR approach to investigate the effects of fiscal policy on environmental pollution in Pakistan. Environ Scie Poll Res 1–14 [ PubMed ]
• Abbass K, Song H, Shah SM, Aziz B. Determinants of Stock Return for Non-Financial Sector: Evidence from Energy Sector of Pakistan. J Bus Fin Aff. 2019; 8 (370):2167–0234. [ Google Scholar ]
• Abbass K, Tanveer A, Huaming S, Khatiya AA (2021c) Impact of financial resources utilization on firm performance: a case of SMEs working in Pakistan
• Abraham E, Chain E. An enzyme from bacteria able to destroy penicillin. 1940. Rev Infect Dis. 1988; 10 (4):677. [ PubMed ] [ Google Scholar ]
• Adger WN, Arnell NW, Tompkins EL. Successful adaptation to climate change across scales. Glob Environ Chang. 2005; 15 (2):77–86. doi: 10.1016/j.gloenvcha.2004.12.005. [ CrossRef ] [ Google Scholar ]
• Akkari C, Bryant CR. The co-construction approach as approach to developing adaptation strategies in the face of climate change and variability: A conceptual framework. Agricultural Research. 2016; 5 (2):162–173. doi: 10.1007/s40003-016-0208-8. [ CrossRef ] [ Google Scholar ]
• Alhassan H (2021) The effect of agricultural total factor productivity on environmental degradation in sub-Saharan Africa. Sci Afr 12:e00740
• Ali A, Erenstein O. Assessing farmer use of climate change adaptation practices and impacts on food security and poverty in Pakistan. Clim Risk Manag. 2017; 16 :183–194. doi: 10.1016/j.crm.2016.12.001. [ CrossRef ] [ Google Scholar ]
• Allen CD, Macalady AK, Chenchouni H, Bachelet D, McDowell N, Vennetier M, Hogg ET. A global overview of drought and heat-induced tree mortality reveals emerging climate change risks for forests. For Ecol Manag. 2010; 259 (4):660–684. doi: 10.1016/j.foreco.2009.09.001. [ CrossRef ] [ Google Scholar ]
• Anwar A, Sinha A, Sharif A, Siddique M, Irshad S, Anwar W, Malik S (2021) The nexus between urbanization, renewable energy consumption, financial development, and CO2 emissions: evidence from selected Asian countries. Environ Dev Sust. 10.1007/s10668-021-01716-2
• Araus JL, Slafer GA, Royo C, Serret MD. Breeding for yield potential and stress adaptation in cereals. Crit Rev Plant Sci. 2008; 27 (6):377–412. doi: 10.1080/07352680802467736. [ CrossRef ] [ Google Scholar ]
• Aron JL, Patz J (2001) Ecosystem change and public health: a global perspective: JHU Press
• Arshad MI, Iqbal MA, Shahbaz M. Pakistan tourism industry and challenges: a review. Asia Pacific Journal of Tourism Research. 2018; 23 (2):121–132. doi: 10.1080/10941665.2017.1410192. [ CrossRef ] [ Google Scholar ]
• Ashbolt NJ. Microbial contamination of drinking water and human health from community water systems. Current Environmental Health Reports. 2015; 2 (1):95–106. doi: 10.1007/s40572-014-0037-5. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Asseng S, Cao W, Zhang W, Ludwig F (2009) Crop physiology, modelling and climate change: impact and adaptation strategies. Crop Physiol 511–543
• Asseng S, Ewert F, Rosenzweig C, Jones JW, Hatfield JL, Ruane AC, Cammarano D. Uncertainty in simulating wheat yields under climate change. Nat Clim Chang. 2013; 3 (9):827–832. doi: 10.1038/nclimate1916. [ CrossRef ] [ Google Scholar ]
• Association A (2020) Climate change is threatening mental health, American Psychological Association, “Kirsten Weir, . from < https://www.apa.org/monitor/2016/07-08/climate-change >, Accessed on 26 Jan 2020.
• Ayers J, Huq S, Wright H, Faisal A, Hussain S. Mainstreaming climate change adaptation into development in Bangladesh. Clim Dev. 2014; 6 :293–305. doi: 10.1080/17565529.2014.977761. [ CrossRef ] [ Google Scholar ]
• Balsalobre-Lorente D, Driha OM, Bekun FV, Sinha A, Adedoyin FF (2020) Consequences of COVID-19 on the social isolation of the Chinese economy: accounting for the role of reduction in carbon emissions. Air Qual Atmos Health 13(12):1439–1451
• Balsalobre-Lorente D, Ibáñez-Luzón L, Usman M, Shahbaz M. The environmental Kuznets curve, based on the economic complexity, and the pollution haven hypothesis in PIIGS countries. Renew Energy. 2022; 185 :1441–1455. doi: 10.1016/j.renene.2021.10.059. [ CrossRef ] [ Google Scholar ]
• Bank W (2008) Forests sourcebook: practical guidance for sustaining forests in development cooperation: World Bank
• Barua S, Valenzuela E (2018) Climate change impacts on global agricultural trade patterns: evidence from the past 50 years. In Proceedings of the Sixth International Conference on Sustainable Development (pp. 26–28)
• Bates AE, Pecl GT, Frusher S, Hobday AJ, Wernberg T, Smale DA, Colwell RK. Defining and observing stages of climate-mediated range shifts in marine systems. Glob Environ Chang. 2014; 26 :27–38. doi: 10.1016/j.gloenvcha.2014.03.009. [ CrossRef ] [ Google Scholar ]
• Battisti DS, Naylor RL. Historical warnings of future food insecurity with unprecedented seasonal heat. Science. 2009; 323 (5911):240–244. doi: 10.1126/science.1164363. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Beesley L, Close PG, Gwinn DC, Long M, Moroz M, Koster WM, Storer T. Flow-mediated movement of freshwater catfish, Tandanus bostocki, in a regulated semi-urban river, to inform environmental water releases. Ecol Freshw Fish. 2019; 28 (3):434–445. doi: 10.1111/eff.12466. [ CrossRef ] [ Google Scholar ]
• Benita F (2021) Human mobility behavior in COVID-19: A systematic literature review and bibliometric analysis. Sustain Cities Soc 70:102916 [ PMC free article ] [ PubMed ]
• Berendonk TU, Manaia CM, Merlin C, Fatta-Kassinos D, Cytryn E, Walsh F, Pons M-N. Tackling antibiotic resistance: the environmental framework. Nat Rev Microbiol. 2015; 13 (5):310–317. doi: 10.1038/nrmicro3439. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Berg MP, Kiers ET, Driessen G, Van DerHEIJDEN M, Kooi BW, Kuenen F, Ellers J. Adapt or disperse: understanding species persistence in a changing world. Glob Change Biol. 2010; 16 (2):587–598. doi: 10.1111/j.1365-2486.2009.02014.x. [ CrossRef ] [ Google Scholar ]
• Blum A, Klueva N, Nguyen H. Wheat cellular thermotolerance is related to yield under heat stress. Euphytica. 2001; 117 (2):117–123. doi: 10.1023/A:1004083305905. [ CrossRef ] [ Google Scholar ]
• Bonacci O. Air temperature and precipitation analyses on a small Mediterranean island: the case of the remote island of Lastovo (Adriatic Sea, Croatia) Acta Hydrotechnica. 2019; 32 (57):135–150. doi: 10.15292/acta.hydro.2019.10. [ CrossRef ] [ Google Scholar ]
• Botzen W, Duijndam S, van Beukering P (2021) Lessons for climate policy from behavioral biases towards COVID-19 and climate change risks. World Dev 137:105214 [ PMC free article ] [ PubMed ]
• Brázdil R, Stucki P, Szabó P, Řezníčková L, Dolák L, Dobrovolný P, Suchánková S. Windstorms and forest disturbances in the Czech Lands: 1801–2015. Agric for Meteorol. 2018; 250 :47–63. doi: 10.1016/j.agrformet.2017.11.036. [ CrossRef ] [ Google Scholar ]
• Brown HCP, Smit B, Somorin OA, Sonwa DJ, Nkem JN. Climate change and forest communities: prospects for building institutional adaptive capacity in the Congo Basin forests. Ambio. 2014; 43 (6):759–769. doi: 10.1007/s13280-014-0493-z. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Bujosa A, Riera A, Torres CM. Valuing tourism demand attributes to guide climate change adaptation measures efficiently: the case of the Spanish domestic travel market. Tour Manage. 2015; 47 :233–239. doi: 10.1016/j.tourman.2014.09.023. [ CrossRef ] [ Google Scholar ]
• Calderini D, Abeledo L, Savin R, Slafer GA. Effect of temperature and carpel size during pre-anthesis on potential grain weight in wheat. J Agric Sci. 1999; 132 (4):453–459. doi: 10.1017/S0021859699006504. [ CrossRef ] [ Google Scholar ]
• Cammell M, Knight J. Effects of climatic change on the population dynamics of crop pests. Adv Ecol Res. 1992; 22 :117–162. doi: 10.1016/S0065-2504(08)60135-X. [ CrossRef ] [ Google Scholar ]
• Cavanaugh KC, Kellner JR, Forde AJ, Gruner DS, Parker JD, Rodriguez W, Feller IC. Poleward expansion of mangroves is a threshold response to decreased frequency of extreme cold events. Proc Natl Acad Sci. 2014; 111 (2):723–727. doi: 10.1073/pnas.1315800111. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Cell CC (2009) Climate change and health impacts in Bangladesh. Clima Chang Cell DoE MoEF
• Chandio AA, Jiang Y, Rehman A, Rauf A (2020) Short and long-run impacts of climate change on agriculture: an empirical evidence from China. Int J Clim Chang Strat Manag
• Chaudhary P, Rai S, Wangdi S, Mao A, Rehman N, Chettri S, Bawa KS (2011) Consistency of local perceptions of climate change in the Kangchenjunga Himalaya landscape. Curr Sci 504–513
• Chien F, Anwar A, Hsu CC, Sharif A, Razzaq A, Sinha A (2021) The role of information and communication technology in encountering environmental degradation: proposing an SDG framework for the BRICS countries. Technol Soc 65:101587
• Cooper C, Booth A, Varley-Campbell J, Britten N, Garside R. Defining the process to literature searching in systematic reviews: a literature review of guidance and supporting studies. BMC Med Res Methodol. 2018; 18 (1):1–14. doi: 10.1186/s12874-018-0545-3. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Costello A, Abbas M, Allen A, Ball S, Bell S, Bellamy R, Kett M. Managing the health effects of climate change: lancet and University College London Institute for Global Health Commission. The Lancet. 2009; 373 (9676):1693–1733. doi: 10.1016/S0140-6736(09)60935-1. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Cruz DLA (2015) Mother Figured. University of Chicago Press. Retrieved from, 10.7208/9780226315072
• Cui W, Ouyang T, Qiu Y, Cui D (2021) Literature Review of the Implications of Exercise Rehabilitation Strategies for SARS Patients on the Recovery of COVID-19 Patients. Paper presented at the Healthcare [ PMC free article ] [ PubMed ]
• Davidson D. Gaps in agricultural climate adaptation research. Nat Clim Chang. 2016; 6 (5):433–435. doi: 10.1038/nclimate3007. [ CrossRef ] [ Google Scholar ]
• Diffenbaugh NS, Singh D, Mankin JS, Horton DE, Swain DL, Touma D, Tsiang M. Quantifying the influence of global warming on unprecedented extreme climate events. Proc Natl Acad Sci. 2017; 114 (19):4881–4886. doi: 10.1073/pnas.1618082114. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Dimri A, Kumar D, Choudhary A, Maharana P. Future changes over the Himalayas: mean temperature. Global Planet Change. 2018; 162 :235–251. doi: 10.1016/j.gloplacha.2018.01.014. [ CrossRef ] [ Google Scholar ]
• Dullinger S, Gattringer A, Thuiller W, Moser D, Zimmermann N, Guisan A. Extinction debt of high-mountain plants under twenty-first-century climate change. Nat Clim Chang: Nature Publishing Group; 2012. [ Google Scholar ]
• Dupuis I, Dumas C. Influence of temperature stress on in vitro fertilization and heat shock protein synthesis in maize (Zea mays L.) reproductive tissues. Plant Physiol. 1990; 94 (2):665–670. doi: 10.1104/pp.94.2.665. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Edreira JR, Otegui ME. Heat stress in temperate and tropical maize hybrids: a novel approach for assessing sources of kernel loss in field conditions. Field Crop Res. 2013; 142 :58–67. doi: 10.1016/j.fcr.2012.11.009. [ CrossRef ] [ Google Scholar ]
• Edreira JR, Carpici EB, Sammarro D, Otegui M. Heat stress effects around flowering on kernel set of temperate and tropical maize hybrids. Field Crop Res. 2011; 123 (2):62–73. doi: 10.1016/j.fcr.2011.04.015. [ CrossRef ] [ Google Scholar ]
• Ellison D, Morris CE, Locatelli B, Sheil D, Cohen J, Murdiyarso D, Pokorny J. Trees, forests and water: Cool insights for a hot world. Glob Environ Chang. 2017; 43 :51–61. doi: 10.1016/j.gloenvcha.2017.01.002. [ CrossRef ] [ Google Scholar ]
• Elsayed ZM, Eldehna WM, Abdel-Aziz MM, El Hassab MA, Elkaeed EB, Al-Warhi T, Mohammed ER. Development of novel isatin–nicotinohydrazide hybrids with potent activity against susceptible/resistant Mycobacterium tuberculosis and bronchitis causing–bacteria. J Enzyme Inhib Med Chem. 2021; 36 (1):384–393. doi: 10.1080/14756366.2020.1868450. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• EM-DAT (2020) EMDAT: OFDA/CRED International Disaster Database, Université catholique de Louvain – Brussels – Belgium. from http://www.emdat.be
• EPA U (2018) United States Environmental Protection Agency, EPA Year in Review
• Erman A, De Vries Robbe SA, Thies SF, Kabir K, Maruo M (2021) Gender Dimensions of Disaster Risk and Resilience
• Fand BB, Kamble AL, Kumar M. Will climate change pose serious threat to crop pest management: a critical review. Int J Sci Res Publ. 2012; 2 (11):1–14. [ Google Scholar ]
• FAO (2018).The State of the World’s Forests 2018 - Forest Pathways to Sustainable Development.
• Fardous S Perception of climate change in Kaptai National Park. Rural Livelihoods and Protected Landscape: Co-Management in the Wetlands and Forests of Bangladesh, 186–204
• Farooq M, Bramley H, Palta JA, Siddique KH. Heat stress in wheat during reproductive and grain-filling phases. Crit Rev Plant Sci. 2011; 30 (6):491–507. doi: 10.1080/07352689.2011.615687. [ CrossRef ] [ Google Scholar ]
• Feliciano D, Recha J, Ambaw G, MacSween K, Solomon D, Wollenberg E (2022) Assessment of agricultural emissions, climate change mitigation and adaptation practices in Ethiopia. Clim Policy 1–18
• Ferreira JJ, Fernandes CI, Ferreira FA (2020) Technology transfer, climate change mitigation, and environmental patent impact on sustainability and economic growth: a comparison of European countries. Technol Forecast Soc Change 150:119770
• Fettig CJ, Reid ML, Bentz BJ, Sevanto S, Spittlehouse DL, Wang T. Changing climates, changing forests: a western North American perspective. J Forest. 2013; 111 (3):214–228. doi: 10.5849/jof.12-085. [ CrossRef ] [ Google Scholar ]
• Fischer AP. Characterizing behavioral adaptation to climate change in temperate forests. Landsc Urban Plan. 2019; 188 :72–79. doi: 10.1016/j.landurbplan.2018.09.024. [ CrossRef ] [ Google Scholar ]
• Flannigan M, Cantin AS, De Groot WJ, Wotton M, Newbery A, Gowman LM. Global wildland fire season severity in the 21st century. For Ecol Manage. 2013; 294 :54–61. doi: 10.1016/j.foreco.2012.10.022. [ CrossRef ] [ Google Scholar ]
• Fossheim M, Primicerio R, Johannesen E, Ingvaldsen RB, Aschan MM, Dolgov AV. Recent warming leads to a rapid borealization of fish communities in the Arctic. Nat Clim Chang. 2015; 5 (7):673–677. doi: 10.1038/nclimate2647. [ CrossRef ] [ Google Scholar ]
• Füssel HM, Hildén M (2014) How is uncertainty addressed in the knowledge base for national adaptation planning? Adapting to an Uncertain Climate (pp. 41–66): Springer
• Gambín BL, Borrás L, Otegui ME. Source–sink relations and kernel weight differences in maize temperate hybrids. Field Crop Res. 2006; 95 (2–3):316–326. doi: 10.1016/j.fcr.2005.04.002. [ CrossRef ] [ Google Scholar ]
• Gambín B, Borrás L. Resource distribution and the trade-off between seed number and seed weight: a comparison across crop species. Annals of Applied Biology. 2010; 156 (1):91–102. doi: 10.1111/j.1744-7348.2009.00367.x. [ CrossRef ] [ Google Scholar ]
• Gampe D, Nikulin G, Ludwig R. Using an ensemble of regional climate models to assess climate change impacts on water scarcity in European river basins. Sci Total Environ. 2016; 573 :1503–1518. doi: 10.1016/j.scitotenv.2016.08.053. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• García GA, Dreccer MF, Miralles DJ, Serrago RA. High night temperatures during grain number determination reduce wheat and barley grain yield: a field study. Glob Change Biol. 2015; 21 (11):4153–4164. doi: 10.1111/gcb.13009. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Garner E, Inyang M, Garvey E, Parks J, Glover C, Grimaldi A, Edwards MA. Impact of blending for direct potable reuse on premise plumbing microbial ecology and regrowth of opportunistic pathogens and antibiotic resistant bacteria. Water Res. 2019; 151 :75–86. doi: 10.1016/j.watres.2018.12.003. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Gleditsch NP (2021) This time is different! Or is it? NeoMalthusians and environmental optimists in the age of climate change. J Peace Res 0022343320969785
• Godfray HCJ, Beddington JR, Crute IR, Haddad L, Lawrence D, Muir JF, Toulmin C. Food security: the challenge of feeding 9 billion people. Science. 2010; 327 (5967):812–818. doi: 10.1126/science.1185383. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Goes S, Hasterok D, Schutt DL, Klöcking M (2020) Continental lithospheric temperatures: A review. Phys Earth Planet Inter 106509
• Gorst A, Dehlavi A, Groom B. Crop productivity and adaptation to climate change in Pakistan. Environ Dev Econ. 2018; 23 (6):679–701. doi: 10.1017/S1355770X18000232. [ CrossRef ] [ Google Scholar ]
• Gosling SN, Arnell NW. A global assessment of the impact of climate change on water scarcity. Clim Change. 2016; 134 (3):371–385. doi: 10.1007/s10584-013-0853-x. [ CrossRef ] [ Google Scholar ]
• Gössling S, Scott D, Hall CM, Ceron J-P, Dubois G. Consumer behaviour and demand response of tourists to climate change. Ann Tour Res. 2012; 39 (1):36–58. doi: 10.1016/j.annals.2011.11.002. [ CrossRef ] [ Google Scholar ]
• Gourdji SM, Sibley AM, Lobell DB. Global crop exposure to critical high temperatures in the reproductive period: historical trends and future projections. Environ Res Lett. 2013; 8 (2):024041. doi: 10.1088/1748-9326/8/2/024041. [ CrossRef ] [ Google Scholar ]
• Grieg E Responsible Consumption and Production
• Gunter BG, Rahman A, Rahman A (2008) How Vulnerable are Bangladesh’s Indigenous People to Climate Change? Bangladesh Development Research Center (BDRC)
• Hall CM, Amelung B, Cohen S, Eijgelaar E, Gössling S, Higham J, Scott D. On climate change skepticism and denial in tourism. J Sustain Tour. 2015; 23 (1):4–25. doi: 10.1080/09669582.2014.953544. [ CrossRef ] [ Google Scholar ]
• Hartmann H, Moura CF, Anderegg WR, Ruehr NK, Salmon Y, Allen CD, Galbraith D. Research frontiers for improving our understanding of drought-induced tree and forest mortality. New Phytol. 2018; 218 (1):15–28. doi: 10.1111/nph.15048. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Hatfield JL, Prueger JH. Temperature extremes: Effect on plant growth and development. Weather and Climate Extremes. 2015; 10 :4–10. doi: 10.1016/j.wace.2015.08.001. [ CrossRef ] [ Google Scholar ]
• Hatfield JL, Boote KJ, Kimball B, Ziska L, Izaurralde RC, Ort D, Wolfe D. Climate impacts on agriculture: implications for crop production. Agron J. 2011; 103 (2):351–370. doi: 10.2134/agronj2010.0303. [ CrossRef ] [ Google Scholar ]
• Hendriksen RS, Munk P, Njage P, Van Bunnik B, McNally L, Lukjancenko O, Kjeldgaard J. Global monitoring of antimicrobial resistance based on metagenomics analyses of urban sewage. Nat Commun. 2019; 10 (1):1124. doi: 10.1038/s41467-019-08853-3. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Huang S (2004) Global trade patterns in fruits and vegetables. USDA-ERS Agriculture and Trade Report No. WRS-04–06
• Huang W, Gao Q-X, Cao G-L, Ma Z-Y, Zhang W-D, Chao Q-C. Effect of urban symbiosis development in China on GHG emissions reduction. Adv Clim Chang Res. 2016; 7 (4):247–252. doi: 10.1016/j.accre.2016.12.003. [ CrossRef ] [ Google Scholar ]
• Huang Y, Haseeb M, Usman M, Ozturk I (2022) Dynamic association between ICT, renewable energy, economic complexity and ecological footprint: Is there any difference between E-7 (developing) and G-7 (developed) countries? Tech Soc 68:101853
• Hubbart JA, Guyette R, Muzika R-M. More than drought: precipitation variance, excessive wetness, pathogens and the future of the western edge of the eastern deciduous forest. Sci Total Environ. 2016; 566 :463–467. doi: 10.1016/j.scitotenv.2016.05.108. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Hussain M, Butt AR, Uzma F, Ahmed R, Irshad S, Rehman A, Yousaf B. A comprehensive review of climate change impacts, adaptation, and mitigation on environmental and natural calamities in Pakistan. Environ Monit Assess. 2020; 192 (1):48. doi: 10.1007/s10661-019-7956-4. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Hussain M, Liu G, Yousaf B, Ahmed R, Uzma F, Ali MU, Butt AR. Regional and sectoral assessment on climate-change in Pakistan: social norms and indigenous perceptions on climate-change adaptation and mitigation in relation to global context. J Clean Prod. 2018; 200 :791–808. doi: 10.1016/j.jclepro.2018.07.272. [ CrossRef ] [ Google Scholar ]
• Intergov. Panel Clim Chang 33 from 10.1017/CBO9781107415324
• Ionescu C, Klein RJ, Hinkel J, Kumar KK, Klein R. Towards a formal framework of vulnerability to climate change. Environ Model Assess. 2009; 14 (1):1–16. doi: 10.1007/s10666-008-9179-x. [ CrossRef ] [ Google Scholar ]
• IPCC (2013) Summary for policymakers. Clim Chang Phys Sci Basis Contrib Work Gr I Fifth Assess Rep
• Ishikawa-Ishiwata Y, Furuya J (2022) Economic evaluation and climate change adaptation measures for rice production in vietnam using a supply and demand model: special emphasis on the Mekong River Delta region in Vietnam. In Interlocal Adaptations to Climate Change in East and Southeast Asia (pp. 45–53). Springer, Cham
• Izaguirre C, Losada I, Camus P, Vigh J, Stenek V. Climate change risk to global port operations. Nat Clim Chang. 2021; 11 (1):14–20. doi: 10.1038/s41558-020-00937-z. [ CrossRef ] [ Google Scholar ]
• Jactel H, Koricheva J, Castagneyrol B (2019) Responses of forest insect pests to climate change: not so simple. Current opinion in insect science [ PubMed ]
• Jahanzad E, Holtz BA, Zuber CA, Doll D, Brewer KM, Hogan S, Gaudin AC. Orchard recycling improves climate change adaptation and mitigation potential of almond production systems. PLoS ONE. 2020; 15 (3):e0229588. doi: 10.1371/journal.pone.0229588. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Jurgilevich A, Räsänen A, Groundstroem F, Juhola S. A systematic review of dynamics in climate risk and vulnerability assessments. Environ Res Lett. 2017; 12 (1):013002. doi: 10.1088/1748-9326/aa5508. [ CrossRef ] [ Google Scholar ]
• Karami E (2012) Climate change, resilience and poverty in the developing world. Paper presented at the Culture, Politics and Climate change conference
• Kärkkäinen L, Lehtonen H, Helin J, Lintunen J, Peltonen-Sainio P, Regina K, . . . Packalen T (2020) Evaluation of policy instruments for supporting greenhouse gas mitigation efforts in agricultural and urban land use. Land Use Policy 99:104991
• Karkman A, Do TT, Walsh F, Virta MP. Antibiotic-resistance genes in waste water. Trends Microbiol. 2018; 26 (3):220–228. doi: 10.1016/j.tim.2017.09.005. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Kohfeld KE, Le Quéré C, Harrison SP, Anderson RF. Role of marine biology in glacial-interglacial CO2 cycles. Science. 2005; 308 (5718):74–78. doi: 10.1126/science.1105375. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Kongsager R. Linking climate change adaptation and mitigation: a review with evidence from the land-use sectors. Land. 2018; 7 (4):158. doi: 10.3390/land7040158. [ CrossRef ] [ Google Scholar ]
• Kurz WA, Dymond C, Stinson G, Rampley G, Neilson E, Carroll A, Safranyik L. Mountain pine beetle and forest carbon feedback to climate change. Nature. 2008; 452 (7190):987. doi: 10.1038/nature06777. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Lamperti F, Bosetti V, Roventini A, Tavoni M, Treibich T (2021) Three green financial policies to address climate risks. J Financial Stab 54:100875
• Leal Filho W, Azeiteiro UM, Balogun AL, Setti AFF, Mucova SA, Ayal D, . . . Oguge NO (2021) The influence of ecosystems services depletion to climate change adaptation efforts in Africa. Sci Total Environ 146414 [ PubMed ]
• Lehner F, Coats S, Stocker TF, Pendergrass AG, Sanderson BM, Raible CC, Smerdon JE. Projected drought risk in 1.5 C and 2 C warmer climates. Geophys Res Lett. 2017; 44 (14):7419–7428. doi: 10.1002/2017GL074117. [ CrossRef ] [ Google Scholar ]
• Lemery J, Knowlton K, Sorensen C (2021) Global climate change and human health: from science to practice: John Wiley & Sons
• Leppänen S, Saikkonen L, Ollikainen M (2014) Impact of Climate Change on cereal grain production in Russia: Mimeo
• Lipczynska-Kochany E. Effect of climate change on humic substances and associated impacts on the quality of surface water and groundwater: a review. Sci Total Environ. 2018; 640 :1548–1565. doi: 10.1016/j.scitotenv.2018.05.376. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• livescience.com. New coronavirus may have ‘jumped’ to humans from snakes, study finds, live science,. from < https://www.livescience.com/new-coronavirus-origin-snakes.html > accessed on Jan 2020
• Lobell DB, Field CB. Global scale climate–crop yield relationships and the impacts of recent warming. Environ Res Lett. 2007; 2 (1):014002. doi: 10.1088/1748-9326/2/1/014002. [ CrossRef ] [ Google Scholar ]
• Lobell DB, Gourdji SM. The influence of climate change on global crop productivity. Plant Physiol. 2012; 160 (4):1686–1697. doi: 10.1104/pp.112.208298. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Ma L, Li B, Zhang T. New insights into antibiotic resistome in drinking water and management perspectives: a metagenomic based study of small-sized microbes. Water Res. 2019; 152 :191–201. doi: 10.1016/j.watres.2018.12.069. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Macchi M, Oviedo G, Gotheil S, Cross K, Boedhihartono A, Wolfangel C, Howell M (2008) Indigenous and traditional peoples and climate change. International Union for the Conservation of Nature, Gland, Suiza
• Mall RK, Gupta A, Sonkar G (2017) Effect of climate change on agricultural crops. In Current developments in biotechnology and bioengineering (pp. 23–46). Elsevier
• Manes S, Costello MJ, Beckett H, Debnath A, Devenish-Nelson E, Grey KA, . . . Krause C (2021) Endemism increases species’ climate change risk in areas of global biodiversity importance. Biol Conserv 257:109070
• Mannig B, Pollinger F, Gafurov A, Vorogushyn S, Unger-Shayesteh K (2018) Impacts of climate change in Central Asia Encyclopedia of the Anthropocene (pp. 195–203): Elsevier
• Martínez-Alvarado O, Gray SL, Hart NC, Clark PA, Hodges K, Roberts MJ. Increased wind risk from sting-jet windstorms with climate change. Environ Res Lett. 2018; 13 (4):044002. doi: 10.1088/1748-9326/aaae3a. [ CrossRef ] [ Google Scholar ]
• Matsui T, Omasa K, Horie T. The difference in sterility due to high temperatures during the flowering period among japonica-rice varieties. Plant Production Science. 2001; 4 (2):90–93. doi: 10.1626/pps.4.90. [ CrossRef ] [ Google Scholar ]
• Meierrieks D (2021) Weather shocks, climate change and human health. World Dev 138:105228
• Michel D, Eriksson M, Klimes M (2021) Climate change and (in) security in transboundary river basins Handbook of Security and the Environment: Edward Elgar Publishing
• Mihiretu A, Okoyo EN, Lemma T. Awareness of climate change and its associated risks jointly explain context-specific adaptation in the Arid-tropics. Northeast Ethiopia SN Social Sciences. 2021; 1 (2):1–18. [ Google Scholar ]
• Millar CI, Stephenson NL. Temperate forest health in an era of emerging megadisturbance. Science. 2015; 349 (6250):823–826. doi: 10.1126/science.aaa9933. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Mishra A, Bruno E, Zilberman D (2021) Compound natural and human disasters: Managing drought and COVID-19 to sustain global agriculture and food sectors. Sci Total Environ 754:142210 [ PMC free article ] [ PubMed ]
• Mosavi SH, Soltani S, Khalilian S (2020) Coping with climate change in agriculture: Evidence from Hamadan-Bahar plain in Iran. Agric Water Manag 241:106332
• Murshed M (2020) An empirical analysis of the non-linear impacts of ICT-trade openness on renewable energy transition, energy efficiency, clean cooking fuel access and environmental sustainability in South Asia. Environ Sci Pollut Res 27(29):36254–36281. 10.1007/s11356-020-09497-3 [ PMC free article ] [ PubMed ]
• Murshed M. Pathways to clean cooking fuel transition in low and middle income Sub-Saharan African countries: the relevance of improving energy use efficiency. Sustainable Production and Consumption. 2022; 30 :396–412. doi: 10.1016/j.spc.2021.12.016. [ CrossRef ] [ Google Scholar ]
• Murshed M, Dao NTT. Revisiting the CO2 emission-induced EKC hypothesis in South Asia: the role of Export Quality Improvement. GeoJournal. 2020 doi: 10.1007/s10708-020-10270-9. [ CrossRef ] [ Google Scholar ]
• Murshed M, Abbass K, Rashid S. Modelling renewable energy adoption across south Asian economies: Empirical evidence from Bangladesh, India, Pakistan and Sri Lanka. Int J Finan Eco. 2021; 26 (4):5425–5450. doi: 10.1002/ijfe.2073. [ CrossRef ] [ Google Scholar ]
• Murshed M, Nurmakhanova M, Elheddad M, Ahmed R. Value addition in the services sector and its heterogeneous impacts on CO2 emissions: revisiting the EKC hypothesis for the OPEC using panel spatial estimation techniques. Environ Sci Pollut Res. 2020; 27 (31):38951–38973. doi: 10.1007/s11356-020-09593-4. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Murshed M, Nurmakhanova M, Al-Tal R, Mahmood H, Elheddad M, Ahmed R (2022) Can intra-regional trade, renewable energy use, foreign direct investments, and economic growth reduce ecological footprints in South Asia? Energy Sources, Part B: Economics, Planning, and Policy. 10.1080/15567249.2022.2038730
• Neuvonen M, Sievänen T, Fronzek S, Lahtinen I, Veijalainen N, Carter TR. Vulnerability of cross-country skiing to climate change in Finland–an interactive mapping tool. J Outdoor Recreat Tour. 2015; 11 :64–79. doi: 10.1016/j.jort.2015.06.010. [ CrossRef ] [ Google Scholar ]
• npr.org. Please Help Me.’ What people in China are saying about the outbreak on social media, npr.org, . from < https://www.npr.org/sections/goatsandsoda/2020/01/24/799000379/please-help-me-what-people-in-china-are-saying-about-the-outbreak-on-social-medi >, Accessed on 26 Jan 2020.
• Ogden LE. Climate change, pathogens, and people: the challenges of monitoring a moving target. Bioscience. 2018; 68 (10):733–739. doi: 10.1093/biosci/biy101. [ CrossRef ] [ Google Scholar ]
• Ortiz AMD, Outhwaite CL, Dalin C, Newbold T. A review of the interactions between biodiversity, agriculture, climate change, and international trade: research and policy priorities. One Earth. 2021; 4 (1):88–101. doi: 10.1016/j.oneear.2020.12.008. [ CrossRef ] [ Google Scholar ]
• Ortiz R. Crop genetic engineering under global climate change. Ann Arid Zone. 2008; 47 (3):343. [ Google Scholar ]
• Otegui MAE, Bonhomme R. Grain yield components in maize: I. Ear growth and kernel set. Field Crop Res. 1998; 56 (3):247–256. doi: 10.1016/S0378-4290(97)00093-2. [ CrossRef ] [ Google Scholar ]
• Pachauri RK, Allen MR, Barros VR, Broome J, Cramer W, Christ R, . . . Dasgupta P (2014) Climate change 2014: synthesis report. Contribution of Working Groups I, II and III to the fifth assessment report of the Intergovernmental Panel on Climate Change: Ipcc
• Pal JK. Visualizing the knowledge outburst in global research on COVID-19. Scientometrics. 2021; 126 (5):4173–4193. doi: 10.1007/s11192-021-03912-3. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Panda R, Behera S, Kashyap P. Effective management of irrigation water for wheat under stressed conditions. Agric Water Manag. 2003; 63 (1):37–56. doi: 10.1016/S0378-3774(03)00099-4. [ CrossRef ] [ Google Scholar ]
• Pärnänen KM, Narciso-da-Rocha C, Kneis D, Berendonk TU, Cacace D, Do TT, Jaeger T. Antibiotic resistance in European wastewater treatment plants mirrors the pattern of clinical antibiotic resistance prevalence. Sci Adv. 2019; 5 (3):eaau9124. doi: 10.1126/sciadv.aau9124. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Parry M, Parry ML, Canziani O, Palutikof J, Van der Linden P, Hanson C (2007) Climate change 2007-impacts, adaptation and vulnerability: Working group II contribution to the fourth assessment report of the IPCC (Vol. 4): Cambridge University Press
• Patz JA, Campbell-Lendrum D, Holloway T, Foley JA. Impact of regional climate change on human health. Nature. 2005; 438 (7066):310–317. doi: 10.1038/nature04188. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Patz JA, Graczyk TK, Geller N, Vittor AY. Effects of environmental change on emerging parasitic diseases. Int J Parasitol. 2000; 30 (12–13):1395–1405. doi: 10.1016/S0020-7519(00)00141-7. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Pautasso M, Döring TF, Garbelotto M, Pellis L, Jeger MJ. Impacts of climate change on plant diseases—opinions and trends. Eur J Plant Pathol. 2012; 133 (1):295–313. doi: 10.1007/s10658-012-9936-1. [ CrossRef ] [ Google Scholar ]
• Peng S, Huang J, Sheehy JE, Laza RC, Visperas RM, Zhong X, Cassman KG. Rice yields decline with higher night temperature from global warming. Proc Natl Acad Sci. 2004; 101 (27):9971–9975. doi: 10.1073/pnas.0403720101. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Pereira HM, Ferrier S, Walters M, Geller GN, Jongman R, Scholes RJ, Cardoso A. Essential biodiversity variables. Science. 2013; 339 (6117):277–278. doi: 10.1126/science.1229931. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Perera K, De Silva K, Amarasinghe M. Potential impact of predicted sea level rise on carbon sink function of mangrove ecosystems with special reference to Negombo estuary, Sri Lanka. Global Planet Change. 2018; 161 :162–171. doi: 10.1016/j.gloplacha.2017.12.016. [ CrossRef ] [ Google Scholar ]
• Pfadenhauer JS, Klötzli FA (2020) Zonal Vegetation of the Subtropical (Warm–Temperate) Zone with Winter Rain. In Global Vegetation (pp. 455–514). Springer, Cham
• Phillips JD. Environmental gradients and complexity in coastal landscape response to sea level rise. CATENA. 2018; 169 :107–118. doi: 10.1016/j.catena.2018.05.036. [ CrossRef ] [ Google Scholar ]
• Pirasteh-Anosheh H, Parnian A, Spasiano D, Race M, Ashraf M (2021) Haloculture: A system to mitigate the negative impacts of pandemics on the environment, society and economy, emphasizing COVID-19. Environ Res 111228 [ PMC free article ] [ PubMed ]
• Pruden A, Larsson DJ, Amézquita A, Collignon P, Brandt KK, Graham DW, Snape JR. Management options for reducing the release of antibiotics and antibiotic resistance genes to the environment. Environ Health Perspect. 2013; 121 (8):878–885. doi: 10.1289/ehp.1206446. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Qasim MZ, Hammad HM, Abbas F, Saeed S, Bakhat HF, Nasim W, Fahad S. The potential applications of picotechnology in biomedical and environmental sciences. Environ Sci Pollut Res. 2020; 27 (1):133–142. doi: 10.1007/s11356-019-06554-4. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Qasim MZ, Hammad HM, Maqsood F, Tariq T, Chawla MS Climate Change Implication on Cereal Crop Productivity
• Rahman M, Alam K. Forest dependent indigenous communities’ perception and adaptation to climate change through local knowledge in the protected area—a Bangladesh case study. Climate. 2016; 4 (1):12. doi: 10.3390/cli4010012. [ CrossRef ] [ Google Scholar ]
• Ramankutty N, Mehrabi Z, Waha K, Jarvis L, Kremen C, Herrero M, Rieseberg LH. Trends in global agricultural land use: implications for environmental health and food security. Annu Rev Plant Biol. 2018; 69 :789–815. doi: 10.1146/annurev-arplant-042817-040256. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Rehman A, Ma H, Ahmad M, Irfan M, Traore O, Chandio AA (2021) Towards environmental Sustainability: devolving the influence of carbon dioxide emission to population growth, climate change, Forestry, livestock and crops production in Pakistan. Ecol Indic 125:107460
• Reichstein M, Carvalhais N. Aspects of forest biomass in the Earth system: its role and major unknowns. Surv Geophys. 2019; 40 (4):693–707. doi: 10.1007/s10712-019-09551-x. [ CrossRef ] [ Google Scholar ]
• Reidsma P, Ewert F, Boogaard H, van Diepen K. Regional crop modelling in Europe: the impact of climatic conditions and farm characteristics on maize yields. Agric Syst. 2009; 100 (1–3):51–60. doi: 10.1016/j.agsy.2008.12.009. [ CrossRef ] [ Google Scholar ]
• Ritchie H, Roser M (2014) Natural disasters. Our World in Data
• Rizvi AR, Baig S, Verdone M. Ecosystems based adaptation: knowledge gaps in making an economic case for investing in nature based solutions for climate change. Gland, Switzerland: IUCN; 2015. p. 48. [ Google Scholar ]
• Roscher C, Fergus AJ, Petermann JS, Buchmann N, Schmid B, Schulze E-D. What happens to the sown species if a biodiversity experiment is not weeded? Basic Appl Ecol. 2013; 14 (3):187–198. doi: 10.1016/j.baae.2013.01.003. [ CrossRef ] [ Google Scholar ]
• Rosenzweig C, Elliott J, Deryng D, Ruane AC, Müller C, Arneth A, Khabarov N. Assessing agricultural risks of climate change in the 21st century in a global gridded crop model intercomparison. Proc Natl Acad Sci. 2014; 111 (9):3268–3273. doi: 10.1073/pnas.1222463110. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Rosenzweig C, Iglesius A, Yang XB, Epstein PR, Chivian E (2001) Climate change and extreme weather events-implications for food production, plant diseases, and pests
• Sadras VO, Slafer GA. Environmental modulation of yield components in cereals: heritabilities reveal a hierarchy of phenotypic plasticities. Field Crop Res. 2012; 127 :215–224. doi: 10.1016/j.fcr.2011.11.014. [ CrossRef ] [ Google Scholar ]
• Salvucci ME, Crafts-Brandner SJ. Inhibition of photosynthesis by heat stress: the activation state of Rubisco as a limiting factor in photosynthesis. Physiol Plant. 2004; 120 (2):179–186. doi: 10.1111/j.0031-9317.2004.0173.x. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Santos WS, Gurgel-Gonçalves R, Garcez LM, Abad-Franch F. Deforestation effects on Attalea palms and their resident Rhodnius, vectors of Chagas disease, in eastern Amazonia. PLoS ONE. 2021; 16 (5):e0252071. doi: 10.1371/journal.pone.0252071. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Sarkar P, Debnath N, Reang D (2021) Coupled human-environment system amid COVID-19 crisis: a conceptual model to understand the nexus. Sci Total Environ 753:141757 [ PMC free article ] [ PubMed ]
• Schlenker W, Roberts MJ. Nonlinear temperature effects indicate severe damages to US crop yields under climate change. Proc Natl Acad Sci. 2009; 106 (37):15594–15598. doi: 10.1073/pnas.0906865106. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Schoene DH, Bernier PY. Adapting forestry and forests to climate change: a challenge to change the paradigm. Forest Policy Econ. 2012; 24 :12–19. doi: 10.1016/j.forpol.2011.04.007. [ CrossRef ] [ Google Scholar ]
• Schuurmans C (2021) The world heat budget: expected changes Climate Change (pp. 1–15): CRC Press
• Scott D. Sustainable Tourism and the Grand Challenge of Climate Change. Sustainability. 2021; 13 (4):1966. doi: 10.3390/su13041966. [ CrossRef ] [ Google Scholar ]
• Scott D, McBoyle G, Schwartzentruber M. Climate change and the distribution of climatic resources for tourism in North America. Climate Res. 2004; 27 (2):105–117. doi: 10.3354/cr027105. [ CrossRef ] [ Google Scholar ]
• Semenov MA. Impacts of climate change on wheat in England and Wales. J R Soc Interface. 2009; 6 (33):343–350. doi: 10.1098/rsif.2008.0285. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Shaffril HAM, Krauss SE, Samsuddin SF. A systematic review on Asian’s farmers’ adaptation practices towards climate change. Sci Total Environ. 2018; 644 :683–695. doi: 10.1016/j.scitotenv.2018.06.349. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Shahbaz M, Balsalobre-Lorente D, Sinha A (2019) Foreign direct Investment–CO2 emissions nexus in Middle East and North African countries: Importance of biomass energy consumption. J Clean Product 217:603–614
• Sharif A, Mishra S, Sinha A, Jiao Z, Shahbaz M, Afshan S (2020) The renewable energy consumption-environmental degradation nexus in Top-10 polluted countries: Fresh insights from quantile-on-quantile regression approach. Renew Energy 150:670–690
• Sharma R. Impacts on human health of climate and land use change in the Hindu Kush-Himalayan region. Mt Res Dev. 2012; 32 (4):480–486. doi: 10.1659/MRD-JOURNAL-D-12-00068.1. [ CrossRef ] [ Google Scholar ]
• Sharma R, Sinha A, Kautish P. Examining the impacts of economic and demographic aspects on the ecological footprint in South and Southeast Asian countries. Environ Sci Pollut Res. 2020; 27 (29):36970–36982. doi: 10.1007/s11356-020-09659-3. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Smit B, Burton I, Klein RJ, Wandel J (2000) An anatomy of adaptation to climate change and variability Societal adaptation to climate variability and change (pp. 223–251): Springer
• Song Y, Fan H, Tang X, Luo Y, Liu P, Chen Y (2021) The effects of severe acute respiratory syndrome coronavirus 2 (SARS-CoV-2) on ischemic stroke and the possible underlying mechanisms. Int J Neurosci 1–20 [ PMC free article ] [ PubMed ]
• Sovacool BK, Griffiths S, Kim J, Bazilian M (2021) Climate change and industrial F-gases: a critical and systematic review of developments, sociotechnical systems and policy options for reducing synthetic greenhouse gas emissions. Renew Sustain Energy Rev 141:110759
• Stewart JA, Perrine JD, Nichols LB, Thorne JH, Millar CI, Goehring KE, Wright DH. Revisiting the past to foretell the future: summer temperature and habitat area predict pika extirpations in California. J Biogeogr. 2015; 42 (5):880–890. doi: 10.1111/jbi.12466. [ CrossRef ] [ Google Scholar ]
• Stocker T, Qin D, Plattner G, Tignor M, Allen S, Boschung J, . . . Midgley P (2013) Climate change 2013: The physical science basis. Working group I contribution to the IPCC Fifth assessment report: Cambridge: Cambridge University Press. 1535p
• Stone P, Nicolas M. Wheat cultivars vary widely in their responses of grain yield and quality to short periods of post-anthesis heat stress. Funct Plant Biol. 1994; 21 (6):887–900. doi: 10.1071/PP9940887. [ CrossRef ] [ Google Scholar ]
• Su H-C, Liu Y-S, Pan C-G, Chen J, He L-Y, Ying G-G. Persistence of antibiotic resistance genes and bacterial community changes in drinking water treatment system: from drinking water source to tap water. Sci Total Environ. 2018; 616 :453–461. doi: 10.1016/j.scitotenv.2017.10.318. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Sunderlin WD, Angelsen A, Belcher B, Burgers P, Nasi R, Santoso L, Wunder S. Livelihoods, forests, and conservation in developing countries: an overview. World Dev. 2005; 33 (9):1383–1402. doi: 10.1016/j.worlddev.2004.10.004. [ CrossRef ] [ Google Scholar ]
• Symanski E, Han HA, Han I, McDaniel M, Whitworth KW, McCurdy S, . . . Delclos GL (2021) Responding to natural and industrial disasters: partnerships and lessons learned. Disaster medicine and public health preparedness 1–4 [ PMC free article ] [ PubMed ]
• Tao F, Yokozawa M, Xu Y, Hayashi Y, Zhang Z. Climate changes and trends in phenology and yields of field crops in China, 1981–2000. Agric for Meteorol. 2006; 138 (1–4):82–92. doi: 10.1016/j.agrformet.2006.03.014. [ CrossRef ] [ Google Scholar ]
• Tebaldi C, Hayhoe K, Arblaster JM, Meehl GA. Going to the extremes. Clim Change. 2006; 79 (3–4):185–211. doi: 10.1007/s10584-006-9051-4. [ CrossRef ] [ Google Scholar ]
• Testa G, Koon E, Johannesson L, McKenna G, Anthony T, Klintmalm G, Gunby R (2018) This article has been accepted for publication and undergone full peer review but has not been through the copyediting, typesetting, pagination and proofreading process, which may lead to differences between this version and the Version of Record. Please cite this article as
• Thornton PK, Lipper L (2014) How does climate change alter agricultural strategies to support food security? (Vol. 1340): Intl Food Policy Res Inst
• Tranfield D, Denyer D, Smart P. Towards a methodology for developing evidence-informed management knowledge by means of systematic review. Br J Manag. 2003; 14 (3):207–222. doi: 10.1111/1467-8551.00375. [ CrossRef ] [ Google Scholar ]
• UNEP (2017) United nations environment programme: frontiers 2017. from https://www.unenvironment.org/news-and-stories/press-release/antimicrobial-resistance - environmental-pollution-among-biggest
• Usman M, Balsalobre-Lorente D (2022) Environmental concern in the era of industrialization: Can financial development, renewable energy and natural resources alleviate some load? Ene Policy 162:112780
• Usman M, Makhdum MSA (2021) What abates ecological footprint in BRICS-T region? Exploring the influence of renewable energy, non-renewable energy, agriculture, forest area and financial development. Renew Energy 179:12–28
• Usman M, Balsalobre-Lorente D, Jahanger A, Ahmad P. Pollution concern during globalization mode in financially resource-rich countries: Do financial development, natural resources, and renewable energy consumption matter? Rene. Energy. 2022; 183 :90–102. doi: 10.1016/j.renene.2021.10.067. [ CrossRef ] [ Google Scholar ]
• Usman M, Jahanger A, Makhdum MSA, Balsalobre-Lorente D, Bashir A (2022a) How do financial development, energy consumption, natural resources, and globalization affect Arctic countries’ economic growth and environmental quality? An advanced panel data simulation. Energy 241:122515
• Usman M, Khalid K, Mehdi MA. What determines environmental deficit in Asia? Embossing the role of renewable and non-renewable energy utilization. Renew Energy. 2021; 168 :1165–1176. doi: 10.1016/j.renene.2021.01.012. [ CrossRef ] [ Google Scholar ]
• Urban MC. Accelerating extinction risk from climate change. Science. 2015; 348 (6234):571–573. doi: 10.1126/science.aaa4984. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Vale MM, Arias PA, Ortega G, Cardoso M, Oliveira BF, Loyola R, Scarano FR (2021) Climate change and biodiversity in the Atlantic Forest: best climatic models, predicted changes and impacts, and adaptation options The Atlantic Forest (pp. 253–267): Springer
• Vedwan N, Rhoades RE. Climate change in the Western Himalayas of India: a study of local perception and response. Climate Res. 2001; 19 (2):109–117. doi: 10.3354/cr019109. [ CrossRef ] [ Google Scholar ]
• Vega CR, Andrade FH, Sadras VO, Uhart SA, Valentinuz OR. Seed number as a function of growth. A comparative study in soybean, sunflower, and maize. Crop Sci. 2001; 41 (3):748–754. doi: 10.2135/cropsci2001.413748x. [ CrossRef ] [ Google Scholar ]
• Vergés A, Doropoulos C, Malcolm HA, Skye M, Garcia-Pizá M, Marzinelli EM, Vila-Concejo A. Long-term empirical evidence of ocean warming leading to tropicalization of fish communities, increased herbivory, and loss of kelp. Proc Natl Acad Sci. 2016; 113 (48):13791–13796. doi: 10.1073/pnas.1610725113. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Verheyen R (2005) Climate change damage and international law: prevention duties and state responsibility (Vol. 54): Martinus Nijhoff Publishers
• Waheed A, Fischer TB, Khan MI. Climate Change Policy Coherence across Policies, Plans, and Strategies in Pakistan—implications for the China-Pakistan Economic Corridor Plan. Environ Manage. 2021; 67 (5):793–810. doi: 10.1007/s00267-021-01449-y. [ PMC free article ] [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Wasiq M, Ahmad M (2004) Sustaining forests: a development strategy: The World Bank
• Watts N, Adger WN, Agnolucci P, Blackstock J, Byass P, Cai W, Cooper A. Health and climate change: policy responses to protect public health. The Lancet. 2015; 386 (10006):1861–1914. doi: 10.1016/S0140-6736(15)60854-6. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Weed AS, Ayres MP, Hicke JA. Consequences of climate change for biotic disturbances in North American forests. Ecol Monogr. 2013; 83 (4):441–470. doi: 10.1890/13-0160.1. [ CrossRef ] [ Google Scholar ]
• Weisheimer A, Palmer T (2005) Changing frequency of occurrence of extreme seasonal temperatures under global warming. Geophys Res Lett 32(20)
• Wernberg T, Bennett S, Babcock RC, De Bettignies T, Cure K, Depczynski M, Hovey RK. Climate-driven regime shift of a temperate marine ecosystem. Science. 2016; 353 (6295):169–172. doi: 10.1126/science.aad8745. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• WHO (2018) WHO, 2018. Antimicrobial resistance
• Wilkinson DM, Sherratt TN. Why is the world green? The interactions of top–down and bottom–up processes in terrestrial vegetation ecology. Plant Ecolog Divers. 2016; 9 (2):127–140. doi: 10.1080/17550874.2016.1178353. [ CrossRef ] [ Google Scholar ]
• Wiranata IJ, Simbolon K. Increasing awareness capacity of disaster potential as a support to achieve sustainable development goal (sdg) 13 in lampung province. Jurnal Pir: Power in International Relations. 2021; 5 (2):129–146. doi: 10.22303/pir.5.2.2021.129-146. [ CrossRef ] [ Google Scholar ]
• Wiréhn L. Nordic agriculture under climate change: a systematic review of challenges, opportunities and adaptation strategies for crop production. Land Use Policy. 2018; 77 :63–74. doi: 10.1016/j.landusepol.2018.04.059. [ CrossRef ] [ Google Scholar ]
• Wu D, Su Y, Xi H, Chen X, Xie B. Urban and agriculturally influenced water contribute differently to the spread of antibiotic resistance genes in a mega-city river network. Water Res. 2019; 158 :11–21. doi: 10.1016/j.watres.2019.03.010. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Wu HX (2020) Losing Steam?—An industry origin analysis of China’s productivity slowdown Measuring Economic Growth and Productivity (pp. 137–167): Elsevier
• Wu H, Qian H, Chen J, Huo C. Assessment of agricultural drought vulnerability in the Guanzhong Plain. China Water Resources Management. 2017; 31 (5):1557–1574. doi: 10.1007/s11269-017-1594-9. [ CrossRef ] [ Google Scholar ]
• Xie W, Huang J, Wang J, Cui Q, Robertson R, Chen K (2018) Climate change impacts on China’s agriculture: the responses from market and trade. China Econ Rev
• Xu J, Sharma R, Fang J, Xu Y. Critical linkages between land-use transition and human health in the Himalayan region. Environ Int. 2008; 34 (2):239–247. doi: 10.1016/j.envint.2007.08.004. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Yadav MK, Singh R, Singh K, Mall R, Patel C, Yadav S, Singh M. Assessment of climate change impact on productivity of different cereal crops in Varanasi. India J Agrometeorol. 2015; 17 (2):179–184. doi: 10.54386/jam.v17i2.1000. [ CrossRef ] [ Google Scholar ]
• Yang B, Usman M. Do industrialization, economic growth and globalization processes influence the ecological footprint and healthcare expenditures? Fresh insights based on the STIRPAT model for countries with the highest healthcare expenditures. Sust Prod Cons. 2021; 28 :893–910. [ Google Scholar ]
• Yu Z, Razzaq A, Rehman A, Shah A, Jameel K, Mor RS (2021) Disruption in global supply chain and socio-economic shocks: a lesson from COVID-19 for sustainable production and consumption. Oper Manag Res 1–16
• Zarnetske PL, Skelly DK, Urban MC. Biotic multipliers of climate change. Science. 2012; 336 (6088):1516–1518. doi: 10.1126/science.1222732. [ PubMed ] [ CrossRef ] [ Google Scholar ]
• Zhang M, Liu N, Harper R, Li Q, Liu K, Wei X, Liu S. A global review on hydrological responses to forest change across multiple spatial scales: importance of scale, climate, forest type and hydrological regime. J Hydrol. 2017; 546 :44–59. doi: 10.1016/j.jhydrol.2016.12.040. [ CrossRef ] [ Google Scholar ]
• Zhao J, Sinha A, Inuwa N, Wang Y, Murshed M, Abbasi KR (2022) Does Structural Transformation in Economy Impact Inequality in Renewable Energy Productivity? Implications for Sustainable Development. Renew Energy 189:853–864. 10.1016/j.renene.2022.03.050

Information

• Author Services

Initiatives

You are accessing a machine-readable page. In order to be human-readable, please install an RSS reader.

All articles published by MDPI are made immediately available worldwide under an open access license. No special permission is required to reuse all or part of the article published by MDPI, including figures and tables. For articles published under an open access Creative Common CC BY license, any part of the article may be reused without permission provided that the original article is clearly cited. For more information, please refer to https://www.mdpi.com/openaccess .

Feature papers represent the most advanced research with significant potential for high impact in the field. A Feature Paper should be a substantial original Article that involves several techniques or approaches, provides an outlook for future research directions and describes possible research applications.

Feature papers are submitted upon individual invitation or recommendation by the scientific editors and must receive positive feedback from the reviewers.

Editor’s Choice articles are based on recommendations by the scientific editors of MDPI journals from around the world. Editors select a small number of articles recently published in the journal that they believe will be particularly interesting to readers, or important in the respective research area. The aim is to provide a snapshot of some of the most exciting work published in the various research areas of the journal.

Original Submission Date Received: .

• Active Journals
• Find a Journal
• Journal Proposal
• Proceedings Series
• For Authors
• For Reviewers
• For Editors
• For Librarians
• For Publishers
• For Societies
• For Conference Organizers
• Open Access Policy
• Institutional Open Access Program
• Special Issues Guidelines
• Editorial Process
• Research and Publication Ethics
• Article Processing Charges
• Testimonials
• Preprints.org
• SciProfiles
• Encyclopedia

Article Menu

• Subscribe SciFeed
• Recommended Articles
• Google Scholar
• on Google Scholar
• Table of Contents

Find support for a specific problem in the support section of our website.

Please let us know what you think of our products and services.

Visit our dedicated information section to learn more about MDPI.

JSmol Viewer

Balancing environmental impact and practicality: a case study on the cement-stabilized rammed earth construction in southeast rural china.

1. Introduction

• Simultaneously achieving twin rural revitalization and dual carbon emission reduction policy objectives.
• The loss of labor fundamentally hampers village behavior associated with human activity.
• China is going through a transition phase from poverty eradication to rural revitalization, and the level of infrastructure development in rural areas is relatively lagging, posing a risk of returning to poverty.
• Industrialized materials and technologies impact traditional construction techniques.
• Increased frequency of unpredictable weather extremes and natural disasters.
• The increased use of multiple channels to obtain information and resources without improving discernment. Although the population has decreased, resource consumption and carbon emissions have increased.

2. Research Progress of Rammed Earth

3. Case Study

3.1. comparative simulation study, 3.2. project case study, existing situation on site, 5. discussion, 6. conclusions, author contributions, institutional review board statement, informed consent statement, data availability statement, acknowledgments, conflicts of interest.

• Wang, X. Research on Symbiotic Development of Urbanand Rural Areas ; College of Public Administration Nanjing Agricultural University: Nanjing, China, 2015. [ Google Scholar ]
• Ministry of Housing and Urban-Rural Development of China. Statistical Yearbook of Urban-Rural Construction 2022 ; China Statistics Press: Beijing, China, 2023. [ Google Scholar ]
• Tang, G. Appropriate Technology System and Construction Mode for Rural Architecture ; Huazhong University of Science and Technology Press Co.: Wuhan, China, 2021. [ Google Scholar ]
• Wang, H.L. An analysis of the reasons for the formation of rural ‘hollow villages’ and countermeasures to solve the problem. Rural. Econ. 2005 , 9 , 21–22. [ Google Scholar ]
• Li, Y.-R.; Cao, L.-Z.; Wang, P.-Y.; Chang, G.-J. Rural living environment improvement and rural revitalization. J. Nat. Resour. 2022 , 37 , 96–109. [ Google Scholar ] [ CrossRef ]
• Liu, Y.; Zang, Y.; Yang, Y. China’s rural revitalization and development: Theory, technology and management. J. Geogr. Sci. 2020 , 30 , 1923–1942. [ Google Scholar ] [ CrossRef ]
• GFDRR; The World Bank. China’s Experience in Disaster Risk Management ; GFDRR: Washington, DC, USA; The World Bank: Washington, DC, USA, 2020. [ Google Scholar ]
• Academy of Disaster Reduction and Emergency Management, Ministry of Emergency Management; Ministry of Education; School of National Safety and Emergency Management, Beijing Normal University; National Disaster Reduction Center of China, Ministry of Emergency Management; International Federation of Red Cross and Red Crescent Societies. Global Natural Disaster Assessment Report ; American Society of Civil Engineers: Reston, VA, USA, 2022. [ Google Scholar ]
• Burroughs, S. Soil Property Criteria for Rammed Earth Stabilization. J. Mater. Civ. Eng. 2008 , 20 , 264–273. [ Google Scholar ] [ CrossRef ]
• Marc Auzet, J.G. Da Bai Yi Phase 2_Synthese on Soil Analysis ; Laboratory report; Kunming, China, 2018. [ Google Scholar ]
• Wang, Y.; Wang, M.; Liu, K.; Pan, W.; Yang, X. Shaking table tests on seismic retrofitting of rammed-earth structures. Bull. Earthq. Eng. 2016 , 15 , 1037–1055. [ Google Scholar ] [ CrossRef ]
• Ciancio, D.; Beckett, C. Rammed Earth Construction: Cutting-Edge Research on Traditional and Modern Rammed Earth ; CRC Press: Boca Raton, FL, USA, 2015. [ Google Scholar ]
• Mustafa, Y.M.H.; Al-Amoudi, O.S.B.; Zami, M.S.; Al-Osta, M.A. Assessment of the Suitability of Earth as a Construction Material from Experimental and Numerical Perspectives: A Critical Review. Int. J. Géoméch. 2023 , 23 , 03123003. [ Google Scholar ] [ CrossRef ]
• Pelé-Peltier, A.; Charef, R.; Morel, J.-C. Factors affecting the use of earth material in mainstream construction: A critical review. Build. Res. Inf. 2023 , 51 , 119–137. [ Google Scholar ] [ CrossRef ]
• Jun, M.; Zhou, T.; Jiang, W.; Lu, L.; Wang, S.; Li, Q. A Study on the Localization of Modern Rammed Earth Technology in Rural Construction and Demonstration Projects. J. Archit. 2016 , 6 , 573. [ Google Scholar ]
• Xu, Y.; Yao, Y. Informal Institutions, Collective Action, and Public Investment in Rural China. Am. Politi. Sci. Rev. 2015 , 109 , 371–391. [ Google Scholar ] [ CrossRef ]
• UNEP. Building Materials and the Climate: Constructing a New Future. In Building Materials and the Climate: Constructing a New Future ; Dyson, A., Keena, N., Lokko, M.-L., Ciardullo, C., Eds.; United Nations Environment Programme: Nairobi, Kenya, 2023. [ Google Scholar ]
• Touati, K.; Benzaama, M.-H.; El Mendili, Y.; Le Guern, M.; Streiff, F.; Goodhew, S. Hygrothermal and Economic Analysis of an Earth-Based Building Using In Situ Investigations and Artificial Neural Network Modeling for Normandy’s Climate Conditions. Sustainability 2023 , 15 , 13985. [ Google Scholar ] [ CrossRef ]
• Ciancio, D.; Jaquin, P.; Walker, P. Advances on the assessment of soil suitability for rammed earth. Constr. Build. Mater. 2013 , 42 , 40–47. [ Google Scholar ] [ CrossRef ]
• Morel, J.C.; Bui, Q.B.; Hamard, E. Weathering and durability of earthen material and structures. In Modern Earth Buildings ; Woodhead Publishing: Delhi, India, 2012; pp. 282–303. [ Google Scholar ]
• Parracha, J.L.; Lima, J.; Freire, M.T.; Ferreira, M.; Faria, P. Vernacular Earthen Buildings from Leiria, Portugal—Material Characterization. Int. J. Arch. Heritage 2021 , 15 , 1285–1300. [ Google Scholar ] [ CrossRef ]
• Ma, C.; Chen, B.; Chen, L. Variables controlling strength development of self-compacting earth-based construction. Constr. Build. Mater. 2016 , 123 , 336–345. [ Google Scholar ] [ CrossRef ]
• Haider, A.B.; Iravanian, A.; Selman, M.H.; Ekinci, A. Using Waste PET Shreds for Soil Stabilization: Efficiency and Durability Assessment. Int. J. Geosynth. Ground Eng. 2023 , 9 , 48. [ Google Scholar ] [ CrossRef ]
• Martín-Del-Rio, J.J.; Canivell, J.; Falcón, R.M. The use of non-destructive testing to evaluate the compressive strength of a lime-stabilised rammed-earth wall: Rebound index and ultrasonic pulse velocity. Constr. Build. Mater. 2020 , 242 , 118060. [ Google Scholar ] [ CrossRef ]
• Malkanthi, S.; Wickramasinghe, W.; Perera, A. Use of construction waste to modify soil grading for compressed stabilized earth blocks (CSEB) production. Case Stud. Constr. Mater. 2021 , 15 , e00717. [ Google Scholar ] [ CrossRef ]
• Fodde, E. Traditional Earthen Building Techniques in Central Asia. Int. J. Archit. Herit. 2009 , 3 , 145–168. [ Google Scholar ] [ CrossRef ]
• Fabbri, A.; Morel, J.C.; Aubert, J.E.; Bui, Q.B.; Gallipoli, D.; Reddy, B. Testing and Characterisation of Earth-Based Building Materials and Elements ; State-of-the-Art Report of the RILEM TC 274-TCE; Springer International Publishing: Berlin/Heidelberg, Germany, 2022. [ Google Scholar ]
• Niroumand, H.; Barcelo, J.A.; Saaly, M. The Role of Archeology on Earth Buildings and Earth Architecture in the World. Indian J. Sci. Technol. 2016 , 9 , 25. [ Google Scholar ] [ CrossRef ]
• Bruno, A.W.; Gallipoli, D.; Perlot, C.; Mendes, J. Mechanical behaviour of hypercompacted earth for building construction. Mater. Struct. 2017 , 50 , 160. [ Google Scholar ] [ CrossRef ]
• Kandamby, G.W.T.C. Long Term Existence of Cement Stabilized Rammed Earth Walls. Eng. J. Inst. Eng. Sri Lanka 2019 , 52 , 37–43. [ Google Scholar ] [ CrossRef ]
• Heringer, A.; Howe, L.B.; Rauch, M. Upscaling Earth: Mateiral, Process, Catalyst ; Gta Verlag: Zurich, Switzerland, 2022. [ Google Scholar ]
• Kosarimovahhed, M.; Toufigh, V. Sustainable usage of waste materials as stabilizer in rammed earth structures. J. Clean. Prod. 2020 , 277 , 123279. [ Google Scholar ] [ CrossRef ]
• Lydia Kiroff, H.R. Sustainable Construction Technologies: Earth Buildings in New Zealand. In Proceedings of the Second International Conference on Sustainable Construction Mateirals and Technologies, Ancona, Italy, 28–30 June 2010. [ Google Scholar ]
• Egenti, C.; Khatib, J.M. Sustainability of compressed earth as a construction material. In Sustainability of Construction Materials ; Woodhead Publishing: Delhi, India, 2016; pp. 309–341. [ Google Scholar ]
• Kutschke, L. Social Life-Cycle Assessment for Building Materials. In Examining the Environmental Impacts of Materials and Buildings ; Brownell, B.E., Ed.; IGI Global: Hershey, PA, USA, 2020; pp. 217–250. [ Google Scholar ]
• Khadka, B. Rammed earth, as a sustainable and structurally safe green building: A housing solution in the era of global warming and climate change. Asian J. Civ. Eng. 2019 , 21 , 119–136. [ Google Scholar ] [ CrossRef ]
• Zhang, Y.; Jiang, S.; Quan, D.; Fang, K.; Wang, B.; Ma, Z. Properties of Sustainable Earth Construction Materials: A State-of-the-Art Review. Sustainability 2024 , 16 , 670. [ Google Scholar ] [ CrossRef ]
• Bui, Q.-B.; Bui, T.-T.; El-Nabouch, R.; Thai, D.-K. Vertical Rods as a Seismic Reinforcement Technique for Rammed Earth Walls: An Assessment. Adv. Civ. Eng. 2019 , 2019 , 1285937. [ Google Scholar ] [ CrossRef ]
• Venkatarama Reddy, B.V. Stabilised soil blocks for structural masonry in earth construction. In Modern Earth Buildings ; Woodhead Publishing: Delhi, India, 2012; pp. 324–363. [ Google Scholar ]
• Silva, R.A.; Oliveira, D.V.; Schueremans, L.; Miranda, T.; Machado, J. Shear behaviour of rammed earth walls repaired by means of grouting. In Proceedings of the 9th International Masonry Conference 2014, Guimarães, Portugal, 7–9 July 2014. [ Google Scholar ]
• El-Nabouch, R.; Bui, Q.-B.; Perrotin, P.; Plé, O. Shear Parameters of Rammed Earth Material: Results from Different Approaches. Adv. Mater. Sci. Eng. 2018 , 2018 , 8214604. [ Google Scholar ] [ CrossRef ]
• Pavan, G.; Ullas, S.; Rao, K.N. Shear behavior of cement stabilized rammed earth assemblages. J. Build. Eng. 2020 , 27 , 100966. [ Google Scholar ] [ CrossRef ]
• Jayasinghe, M.T.R.; Jayasinghe, C.; Kariyawasam, K.K.G.K.D.; De Silva, L.I.N. Semi-Tiered Housing for Laterite Earth Sloping Lands-A Sustainable Solution with Alternative Materials and Methods. J. Green Build. 2018 , 13 , 56–72. [ Google Scholar ] [ CrossRef ]
• Matos, A.M.; Varum, H. Self-Compacting Earth-Based Composites: Mixture Design and Multi-Performance Characterisation. Buildings 2022 , 12 , 612. [ Google Scholar ] [ CrossRef ]
• Laghi, V.; Palermo, M.; Trombetti, T.; Schildkamp, M. Seismic-Proof Buildings in Developing Countries. Front. Built Environ. 2017 , 3 , 49. [ Google Scholar ] [ CrossRef ]
• Correia, M.; Lourenco, P.B.; Varum, H. Seismic Retrofitting_Learning from Vernacular Architecture ; CRC Press: Boca Raton, FL, USA, 2015. [ Google Scholar ]
• Preciado, A.; Santos, J.C. Rammed earth sustainability and durability in seismic areas as a building material. IOP Conf. Ser. Earth Environ. Sci. 2020 , 410 , 012108. [ Google Scholar ] [ CrossRef ]
• Mileto, C.; Vegas, F.; Soriano, L.G.; Cristini, V. Vernacular Architecture:Towards a Sustainable Future ; CRC Press: Boca Raton, FL, USA, 2014. [ Google Scholar ]
• Niroumand, H.; Zain, M.; Jamil, M. Various Applications of Earth Architecture. Procedia Soc. Behav. Sci. 2013 , 89 , 231–236. [ Google Scholar ] [ CrossRef ]
• Adam, E.; Jones, P. Thermophysical properties of stabilised soil building blocks. Build. Environ. 1995 , 30 , 245–253. [ Google Scholar ] [ CrossRef ]
• Petcu, C.; Dobrescu, C.F.; Dragomir, C.S.; Ciobanu, A.A.; Lăzărescu, A.V.; Hegyi, A. Thermophysical Characteristics of Clay for Efficient Rammed Earth Wall Construction. Materials 2023 , 16 , 6015. [ Google Scholar ] [ CrossRef ] [ PubMed ]
• Chintha Jayasinghe, D.J. Buddhika Dissanayake, thermal performance of composite walls made out of recycled building wastes and stabilized rammed earth. In Proceedings of the NBRO Research Symposium 2015—Resilient Built Environment, Colombo, Sri Lanka, 22 December 2015. [ Google Scholar ]
• Leitão, D.; Barbosa, J.; Soares, E.; Miranda, T.; Cristelo, N.; Briga-Sá, A. Thermal performance assessment of masonry made of ICEB’s stabilised with alkali-activated fly ash. Energy Build. 2017 , 139 , 44–52. [ Google Scholar ] [ CrossRef ]
• Tinsley, J.; Pavía, S. Thermal performance and fitness of glacial till for rammed earth construction. J. Build. Eng. 2019 , 24 , 100727. [ Google Scholar ] [ CrossRef ]
• Carrobé, A.; Rincón, L.; Martorell, I. Thermal Monitoring and Simulation of Earthen Buildings: A Review. Energies 2021 , 14 , 2080. [ Google Scholar ] [ CrossRef ]
• Navarro, L.; de Gracia, A.; Niall, D.; Castell, A.; Browne, M.; McCormack, S.J.; Griffiths, P.; Cabeza, L.F. Thermal energy storage in building integrated thermal systems: A review. Part 2. Integration as passive system. Renew. Energy 2016 , 85 , 1334–1356. [ Google Scholar ] [ CrossRef ]
• Lovec, V.B.; Jovanovic-Popovic, M.; Zivkovic, B.D. The thermal behavior of rammed earth wall in traditional house in Vojvodina: Thermal mass as a key element for thermal comfort. Therm. Sci. 2018 , 22 (Suppl. S4), S1143–S1155. [ Google Scholar ] [ CrossRef ]
• Samadianfard, S.; Toufigh, V. Stabilization effect on the hygrothermal performance of rammed earth materials. Constr. Build. Mater. 2023 , 409 , 134025. [ Google Scholar ] [ CrossRef ]
• Marais, P.; Littlewood, J.; Karani, G. The use of polymer stabilised earth foundations for rammed earth construction. In Proceedings of the 7th International Conference on Sustainability and Energy in Buildings (SEB), Lisbon, Portugal, 1–3 July 2015; Elsevier Science Bv: Amsterdam, The Netherlands, 2015. [ Google Scholar ]
• Ciurileanu, G.T.; Horvath, I.B. The Use of Cement Stabilized Rammed Earth for Building a Vernacular Modern House. Bul. Institutului Politeh. Din Lasi. Sect. Constr. Arhit. 2012 , 25 , 37. [ Google Scholar ]
• Niroumand, H.; Akbari, R.; Khanlari, K.; Gültekin, A.B.; Barcelo, J.A. A systematic literature review of rammed earth walls. Soil Mech. Found. Eng. 2021 , 58 , 295–301. [ Google Scholar ] [ CrossRef ]
• Marsh, A.T.M.; Kulshreshtha, Y. The state of earthen housing worldwide: How development affects attitudes and adoption. Build. Res. Inf. 2021 , 50 , 485–501. [ Google Scholar ] [ CrossRef ]
• Ciancio, D.; Boulter, M. Stabilised rammed earth: A case study in Western Australia. Proc. Inst. Civ. Eng. Eng. Sustain. 2012 , 165 , 141–154. [ Google Scholar ] [ CrossRef ]
• Abd El Rahman, M.A. A Review of the Construction Techniques for Earthen Buildings, with a Brief Analysis of the Case of the Kingdom of Saudi Arabia. Ph.D. Dissertation, Heriot-Watt University, Edinburgh, Scotland, 2012. [ Google Scholar ]
• Zhou, T.; Peng, D.; Mu, J.; Hugo, C.G.; Quentin, A.R. Research and Application of Modern Rammed Earth Wall Construction Technology. Constr. Technol. 2012 , 41 , 370. [ Google Scholar ]
• Giuffrida, G.; Caponetto, R.; Cuomo, M. An overview on contemporary rammed earth buildings: Technological advances in production, construction and material characterization. In Proceedings of the SBE19 Milan—Resilient Built Environment for Sustainable Mediterranean Countries, Milan, Italy, 4–5 September 2019. [ Google Scholar ]
• King, B. Review of Earthen Building Codes and Standards from Around the World ; Ecological Building Network: San Rafael, CA, USA, 2019. [ Google Scholar ]
• Thompson, D.; Augarde, C.; Osorio, J.P. A review of current construction guidelines to inform the design of rammed earth houses in seismically active zones. J. Build. Eng. 2022 , 54 , 104666. [ Google Scholar ] [ CrossRef ]
• Maniatidis, V.; Walker, P. A Review of Rammed Earth Construction for DTi Partners in Innovation Project Developing Rammed Earth for UK Housing ; University of Bath: Bath, UK, 2003. [ Google Scholar ]
• NZS 4297:1998 ; NZD4297-1998-Engineering Design of Earth Buildings [Building Code Compliance Documents B1 (VM1), B2 (AS1)]. Standards New Zealand: Wellington, New Zealand, 1998.
• Andrew Alcorn, P.W. New Zealand Building Materials Embodied Energy Coefficients Database Volume II—Coefficients ; Centre for Building Performance Research Victoria University of Wellington: Wellington, New Zealand, 1998. [ Google Scholar ]
• Schroeder, H. Modern earth building codes, standards and normative development. In Modern Earth Buildings ; Woodhead Publishing: Delhi, India, 2012; pp. 72–109. [ Google Scholar ]
• Fulton, L.; Beauvais, B.; Brooks, M.; Kruse, S.; Lee, K. Sustainable Residential Building Considerations for Rural Areas: A Case Study. Land 2020 , 9 , 152. [ Google Scholar ] [ CrossRef ]
• Adegun, O.B.; Adedeji, Y.M.D. Review of economic and environmental benefits of earthen materials for housing in Africa. Front. Arch. Res. 2017 , 6 , 519–528. [ Google Scholar ] [ CrossRef ]
• van Oorschot, J.; Sprecher, B.; Rijken, B.; Witteveen, P.; Blok, M.; Schouten, N.; van der Voet, E. Toward a low-carbon and circular building sector: Building strategies and urbanization pathways for the Netherlands. J. Ind. Ecol. 2023 , 27 , 535–547. [ Google Scholar ] [ CrossRef ]
• Ben-Alon, L.; Loftness, V.; Harries, K.A.; Hameen, E.C. Integrating Earthen Building Materials and Methods into Mainstream Construction Using Environmental Performance Assessment and Building Policy. IOP Conf. Series Earth Environ. Sci. 2019 , 323 , 012139. [ Google Scholar ] [ CrossRef ]
• Jun, M. Exploring, Renewing and Inheriting the Tradition of Earthen Construction. Archit. J. 2016 , 4 , 1–7. [ Google Scholar ]
• Rael, R. Earth Architecture ; Lee, L., Ball, D., Eds.; Princeton Architectural Press: New York, NY, USA, 2009. [ Google Scholar ]
• Jaquin, P. History of earth building techniques. In Modern Earth Buildings ; Woodhead Publishing: Delhi, India, 2012; pp. 307–323. [ Google Scholar ]
• UNESCO WHC. World Heritage Earthen Architecture Programme (WHEAP). 2017. Available online: https://whc.unesco.org/en/earthen-architecture/ (accessed on 2 May 2024).
• Petrovic, B.; Myhren, J.A.; Zhang, X.; Wallhagen, M.; Eriksson, O. Life Cycle Assessment of Building Materials for a Single-family House in Sweden. Energy Procedia 2019 , 158 , 3547–3552. [ Google Scholar ] [ CrossRef ]
• Han, T.; Huang, Q.; Zhang, A.; Zhang, Q. Simulation-Based Decision Support Tools in the Early Design Stages of a Green Building—A Review. Sustainability 2018 , 10 , 3696. [ Google Scholar ] [ CrossRef ]
• Tartarini, F.; Schiavon, S.; Cheung, T.; Hoyt, T. CBE Thermal Comfort Tool: Online tool for thermal comfort calculations and visualizations. SoftwareX 2020 , 12 , 100563. [ Google Scholar ] [ CrossRef ]
• Betti, G.; Tartarini, F.; Nguyen, C.; Schiavon, S. CBE Clima Tool: A free and open-source web application for climate analysis tailored to sustainable building design. Build. Simul. 2024 , 17 , 493–508. [ Google Scholar ] [ CrossRef ]
• Sun, F. Chinese Climate and Vernacular Dwellings. Buildings 2013 , 3 , 143–172. [ Google Scholar ] [ CrossRef ]
• Chao, Q.C. China Climate Bulletin (2022) ; Meteorological Press: Beijing, China, 2023. [ Google Scholar ]

Click here to enlarge figure

Share and Cite

Dai, S.; Bai, W.; Xiao, J. Balancing Environmental Impact and Practicality: A Case Study on the Cement-Stabilized Rammed Earth Construction in Southeast Rural China. Sustainability 2024 , 16 , 8731. https://doi.org/10.3390/su16208731

Dai S, Bai W, Xiao J. Balancing Environmental Impact and Practicality: A Case Study on the Cement-Stabilized Rammed Earth Construction in Southeast Rural China. Sustainability . 2024; 16(20):8731. https://doi.org/10.3390/su16208731

Dai, Shan, Wenfeng Bai, and Jing Xiao. 2024. "Balancing Environmental Impact and Practicality: A Case Study on the Cement-Stabilized Rammed Earth Construction in Southeast Rural China" Sustainability 16, no. 20: 8731. https://doi.org/10.3390/su16208731

Article Metrics

Article access statistics, further information, mdpi initiatives, follow mdpi.

Subscribe to receive issue release notifications and newsletters from MDPI journals