Solid Waste: An Environmental Issue
Apurba Koley & Ankita Laha*
Introduction
Introduction
Unwanted solid materials generated from human
activities in residential industrial or commercial area which being no longer of value for
the respective economic, physiological or technological process, are removed
from it is called Solid Waste. Solid
waste in a broader sense is understood as any household, industrial and
agricultural materials that have been used up. It predominantly includes food
wastes, yard wastes, containers and product packaging, and other miscellaneous
inorganic wastes from residential, commercial, institutional, and industrial
sources. It may be categorized in three ways.
According to its: origin (domestic, industrial, commercial, construction or
institutional), contents (organic material, glass, metal, plastic paper etc.), hazard
potential (toxic, non-toxin, flammable, radioactive, infectious etc.).
India is rapidly
shifting from agricultural-based nation to industrial and services-oriented
country. About 31.2% population is now living in urban areas. Over 377 million
urban people are living in 7,935 towns/cities. India is a vast country divided
into 29 States and 7 Union Territories (UTs). There are three mega
cities—Greater Mumbai, Delhi, and Kolkata—having population of more than 10
million, 53 cities have more than 1 million population, and 415 cities having
population 100,000 or more (Census, 2011a). The cities having population more than
10 million are basically State capitals, Union Territories, and other
business/industrial-oriented centers. India has different geographic and
climatic regions (tropical wet, tropical dry, subtropical humid climate, and mountain
climate) and four seasons (winter, summer, rainy, and autumn) and accordingly
residents living in these zones have different consumption and waste generation
pattern.( Joshi, 2016).
Per
capita waste generation rate:
Source: *CPCB report (2000) and **Calculated from R.K. Annepu (2012)
Sources and Generation of
Solid Waste
Every day, tonnes of solid waste are
disposed at various landfill sites. This waste comes from homes, shops,
industries, hospitals and various agricultural related activities. The combined
effects of population explosion and changing modern living standard have had a
cumulative effect in the generation of a large amount of various types of
wastes. Solid waste can be classified into different types depending on their
sources:
1. Municipal Solid waste;
2. Hazardous Waste;
3. Biomedical Waste;
4. Industrial Waste;
5. Agricultural Waste;
Municipal Solid waste:
Municipal solid waste is the wastes
which are coming from household works to industrial works of a municipal area. Municipal solid
waste (MSW) or urban solid waste is normally comprised of food wastes, rubbish,
demolition and construction wastes, street sweepings, garden wastes, abandoned
vehicles and appliances, and treatment plant residues. Quantity and
composition of MSW vary greatly for different municipalities and time of the
year. Factors influencing the characteristics of MSW are climate, social customs,
per capita income, and degree of urbanization and industrialization (Singh
et.al, 2014).
As per estimates more than 55 million tons of MSW is generated in India per
year; the yearly increase is estimated to be about 5%. It is estimated that
solid waste generated in small, medium and large cities and towns in India is
about 0.1 kg, 0.3 – 0.4 kg and 0.5 kg per capita per day respectively. The
estimated annual increase in per capita waste generation is about 1.33 % per
year. In India, the biodegradable portion dominates the bulk of MSW. This is
mainly due to food and yard waste. With rising urbanization and change in
lifestyle and food habits, the amount of municipal solid waste has been
increasing rapidly and its composition has been changing.
Statistics of MSW generated in different states in India (CPCB
2000,2013)
The sources of
solid wastes have been consistent, dependent on sectors and activities and
these include the following
.
(i)
Residential: This refers to
wastes from dwellings, apartments, etc., and consists of leftover food,
vegetable peels, plastic, clothes, ashes, etc.
(ii)
Commercial:
This refers to wastes consisting of leftover food, glasses, metals, ashes,
etc., generated from stores, restaurants, markets, hotels, motels, auto-repair
shops, medical facilities, etc.
(iii)
Institutional: This mainly
consists of paper, plastic, glasses, etc., generated from educational,
administrative and public buildings such as schools, colleges, offices,
prisons, etc.
(iv)
Industrial: This mainly
consists of process wastes, ashes, demolition and construction wastes,
hazardous wastes, etc., due to industrial activities.
(v)
Open areas: this includes
wastes from areas such as Streets, alleys, parks, vacant lots, playgrounds,
beaches, highways, recreational areas, etc. (Tchobanoglous, et al., 1977)
Hazardous Waste:
The
first few attempts to quantify hazardous waste generation in the country remain
limited to indirect estimations. For instance, using the correlation between
economic activity and hazardous waste generation established by the Organization
for Economic Cooperation and Development (OECD), the reported generation of
hazardous waste was about 0.3 million tonnes per annum in 1984. World Bank
estimates place this at approximately 4 million tonnes annually for the year
1995. These scattered inventories were not very useful in designing hazardous
waste strategies for the country since hazardous waste generation is very
dynamic owing to the intense growth in industrial activities taking place. In
order to generate an updated inventory for hazardous waste in the country, an
exercise in different states of India was initiated by the CPCB (Central
Pollution Control Board) in the year 1993. The present information on total
hazardous waste generated from industries and facilities available for its
disposal in Indian states has been collected by the MoEF through the respective
SPCBs (state pollution control boards). The state-wise status of number of
units generating hazardous waste as well as the quantity of waste generated
till 24 March 2000, for recyclable, incinerable and disposable waste types.
In total,
at present, around 7.2 million tonnes of hazardous waste is generated in the
country of which 1.4 million tonnes is recyclable, 0.1 million tonnes is
incinerable and 5.2 million tonnes is destined for disposal on land (MoEF
2000). As
per the information provided by the MoEF, there are 323 hazardous waste
recycling units in India, and of these 303 recycling units use indigenous raw
material while 20 depend on imported recyclable wastes. The status of hazardous
waste imported for recycling and recovery of mostly metallic constituents in
country is presented. The major types of hazardous waste imported by the
country include battery scrap, lead and zinc dross, ash, skimmings and residues
and galvanised zinc.
The
Environmental Protection Agency (EPA) has established two categories of
hazardous wastes: characteristic and listed. A waste can be both a
characteristic hazardous waste and a listed hazardous waste. Each
characteristic and each listing has a waste code associated with it. These
waste codes should be used by the generator on hazardous waste manifests, land
disposal restriction (LDR) forms and on any waste determination documents, such
as those provided with the PDEQ Hazardous Waste Determinations and Documentation
technical guidance document (PDEQ).
Characteristic
Hazardous Waste A waste can exhibit the characteristics of:
• Ignitability
(waste code D001);
• Corrosively (waste code D002);
• Reactivity (waste code D003); and/or
• Toxicity
(waste codes D004 to D043).
The first three
characteristics are fairly easy to determine: Ignitable hazardous waste has a flashpoint of less than 140 degrees
Fahrenheit. Corrosive hazardous waste has a pH of 0 to 2 or 12.5 to 14. Reactive hazardous waste is waste that
is normally unstable, reacts violently with water or corrosive materials, or is
capable of detonation or explosion when exposed to heat or flame. There is no
analytical test currently approved by the EPA to determine if a waste is
reactive. The fourth characteristic toxic
hazardous waste is more difficult to determine. EPA has set regulatory
limits for 40 toxic compounds. To determine if a waste meets or exceeds these
regulatory limits, a representative sample of the waste should be collected and
submitted to an ADHS-certified laboratory. The laboratory should prepare the
sample for analysis using the Toxicity Characteristic Leaching Procedure (TCLP)
extraction method to analyze the sample, using EPA-approved test methods, for
the contaminants.(Characteristic
and Listed Hazardous Wastes: Technical Guidance)
Biomedical Waste
According
to Biomedical Waste (Management
and Handling) Rules, 1998 of India “Any waste which
is generated during the diagnosis, treatment or immunization of human beings or
animals or in research activities pertaining thereto or in the production or
testing of biologicals.”
Medical centers including hospitals,
clinics and places where diagnosis and treatment are conducted generate wastes
that are highly hazardous and put people under risk of fatal diseases. Biomedical waste may be solid or liquid. Examples of
infectious waste include discarded blood, sharps, unwanted microbiological cultures and stocks, identifiable body parts (including
those as a result of amputation), other
human or animal tissue, used bandages and
dressings, discarded gloves, other medical supplies that may have been in
contact with blood and body fluids, and
laboratory waste that exhibits the characteristics described above. Waste
sharps include potentially contaminated used (and unused discarded)
needles, scalpels, lancets and other
devices capable of penetrating skin.
While waste management has become a
critical issue which has taken a central place in the national health policies
of developed nations and is attracting considerable interest, in most
developin6ig countries like Nigeria, the handling and treatment of municipal
solid waste (MSW) or domestic waste have not received sufficient attention. (Yelebe
et. al, 2012). Proper management of hospital waste is essential to maintain
hygiene, aesthetics, cleanliness and control of environmental pollution. The
hospital waste like body parts, organs, tissues, blood and body fluids along
with soiled linen, cotton, bandage and plaster casts from infected and
contaminated areas are very essential to be properly collected, segregated,
stored, transported, treated and disposed of in safe manner to prevent hospital
acquired infection.(Barr et. al ,2005 ;
Batterman , 2004 ; Chauhan et. al ,2002.) The segregation of various types of
waste into their different categories according to their treatment/disposal
option was done at the point of generation in color coded plastic bags and
containers, to Protect waste handlers and the public from possible injury and
disease that could result from exposure to the waste and Avoid attraction to
rodents and vermin. Hospital solid waste were observed to be collected in an
open dumping site within the Hospital premises and burnt openly. Sorting of
waste at source of generation with pretreatment in hospital only before
disposal would be the best option.
Fig : Colour coding-biomedical Waste
(management and handling rules,1998)
In India, the Bio
Medical Waste Management Rules, 1998 and further amendments were passed for the
regulation of bio medical waste management. Each state's Pollution Control
Board or Pollution control Committee will be liable for implementing the new
legislation in India. There are a number of special disposal methods, yet most
are harmful rather than helpful. If body fluids are nearby, the substance
desires to be incinerated or put into an autoclave. Although this is the
appropriate method, most medical facilities fail to follow the system. It is
often found that biomedical waste is put into the ocean, where it ultimately
washes up on shore, or in landfills due to inappropriate sorting when in the
medical facility. Improper disposal can lead to many diseases in animals as
well as humans (Ganesh C.P , Bio-Medical Waste Management System). Rules and
guidelines in opposition to Biomedical Waste Management System,
1. The Air (Preclusion
and Organize of Pollution) Act 1981
2. The Environment
(Security) Act 1986
3. The Dangerous Waste
(Managing & Handling) Rules 1989
4. The National
Environmental Tribunal Act 1995
5. The Biomedical Waste
(Managing & Behaviour) Rules 1998
6. The Municipal Solid
Waste (Management & Handling) Rules 2000.
Industrial Waste
Environmental pollution is the major
problem associated with rapid industrialisation, urbanisation and rise in
living standards of people. For
developing countries, industrialisation was must and still this activity very
much demands to build self-reliant and in uplifting nation’s economy. However, industrialisation on the other hand
has also caused serious problems relating to environmental pollution. Current
technology allows, with lower or higher costs and with some exceptions, most
waste to be recycled. Moreover, it is a more complex issue when the combination
of several techniques is required for optimising the process, thus affecting
their viability and, ultimately, their profitability. In turn, each of these
processes can be a new waste generator, often with very different
characteristics from those at the starting point, entering a complex spiral,
which can be approached in many different ways.
As a result, numerous studies have
examined what strategies companies can follow and have proposed methods to
assess the performance of technologies and treatments used (Coelho et al.,
2012) or indexes also to allow the assessment of destination or end use of
solid waste (Coelho et al., 2011). The same problem has been addressed in the
case of municipal solid waste (MSW) (Consonni et al., 2011; Santiago and Dias,
2012), perhaps with greater intensity owing to the existence of policies that
set specific targets for recycling and MSW recovery (Cucchiella et al., 2012;
European Union UE, 2008; Stanic-Maruna and Fellner, 2012). A usual approach is
the use of life cycle analysis (LCA) (Buttol et al., 2007; Kirkeby et al.,
2007; Massarutto et al., 2011; Song et al., 2013), in order to assess or
compare products or processes.
Source: National Waste Management Council-Ministry of Environment and Forests-1990/1999
Agricultural Waste
Agricultural
wastes are defined as the residues from the growing and processing of raw
agricultural products such as fruits, vegetables, meat, poultry, dairy
products, and crops. They are the non-product outputs of production and
processing of agricultural products that may contain material that can benefit
man but whose economic values are less than the cost of collection,
transportation, and processing for beneficial use. Their composition will
depend on the system and type of agricultural activities and they can be in the
form of liquids, slurries, or solids. Agricultural waste otherwise called
agro-waste is comprised of animal waste (manure, animal carcasses), food
processing waste (only 20% of maize is canned and 80% is waste), crop waste
(corn stalks, sugarcane bagasse, drops and culls from fruits and vegetables,
prunings) and hazardous and toxic agricultural waste (pesticides, insecticides
and herbicides, etc). Estimates of agricultural waste arising are rare, but
they are generally thought of as contributing a significant proportion of the
total waste matter in the developed world. Expanding agricultural production
has naturally resulted in increased quantities of livestock waste, agricultural
crop residues and agro-industrial by-products. There is likely to be a
significant increase in agricultural wastes globally if developing countries
continue to intensify farming systems (Obi et. al, 2016). As earlier noted, agricultural development is usually
accompanied by wastes from the irrational application of intensive farming
methods and the abuse of chemicals used in cultivation, remarkably affecting
rural environments in particular and the global environmental in general. The
waste generated is dependent on the type of agricultural activities carried out
i.e. Wastes from Cultivation Activities, Wastes from Livestock
Production, waste from Aquaculture.
*M.Sc. (Sem II)
Department of Environmental Studies,
Visva-Bharati References
- Annepu, R. K. (2012). Sustainable solid waste management in India, Waste-to-Energy Research and Technology Council (WTERT). City of New York: Columbia University.
- Buttol P, Masoni P, Bonoli A, et al. (2007) LCA of integrated MSW management systems: Case study of the Bologna District. Waste Management 27: 1059–1070.
- Census. (2011). Provisional population totals, India. Retrieved from
- Characteristic and Listed Hazardous Wastes: Technical Guidance, Pima Country Department of Environmental Quality Hazardous Waste Generator Programme,
- Coelho HMG, Lange LC and Coelho LMG (2012) Proposal of an environmental performance index to assess solid waste treatment technologies. Waste Management 32: 1473–1481.
- Coelho HMG, Lange LC, Jesus LFL, et al. (2011) Proposta de um Índice de Destinação de Resíduos Sólidos Industriais. Engenharia Sanitaria e Ambiental. 16: 307–316.
- Consonni S, Giugliano M, Massarutto A, et al. (2011) Material and energy recovery in integrated waste management systems: Project overview and main results. Waste Management 31: 2057–2065.
- CPCB. (2000). Status of solid waste generation, collection, treatment and disposal in meterocities (Series: CUPS/46/1999-2000).
- CPCB. (2013). Status report on municipal solid waste management. Retrieved from http://www.cpcb.nic.in/divisionsofheadoffice/pcp/MSW_Report.pdfhttp://pratham.org/images/paper_on_ragpickers.pdf
- Cucchiella F, D’Adamo I and Gastaldi M (2012) Municipal waste management and energy recovery in an Italian region. Waste Management & Research 30: 1290–1298.
- Dr.C.Periya Ganesh, “Bio-Medical Waste Management System”, SSRG International Journal of Nursing and Health Science (SSRG-IJNHS) – volume 1 Issue1June 2015.
- http://censusindia.gov.in/2011-prov-results/ datafiles/india/povpoputotalpresentation2011.pdf
- M.S. Chauhan, and K. Malviya, (2002)Existing solid waste management in hospitals of Indore city, Indian J. Environ. Sci, vol. 6, pp. 43-49.
- MoEF (2000) Draft on Status of Implementation of the Hazardous Waste Rules, 1989. New Delhi: Ministry of Environment and Forests Retrieved From http://www.eai.in/ref/ae/wte/typ/clas/msw.html
- S. Barr, A. Gilg, and N. Ford, (2005)Defining the multidimensional aspects of household waste management: a study of reported behaviour in Devon‖ Res Conserv Recycl, vol. 45(2), pp. 172–92.
- S. Batterman, (2004)Findings on an Assessment of Small-scale Incinerators for Health-care Waste. Water, Sanitation and Health Protection of the human environment. World Health Organization Geneva, 01-07.
- Tchobanoglous, G., Theisen, H., and Eliassan, R. 1977. Solid WastesEngineering Principles and Management Issues, McGraw-Hill Book Company, New York. Retrieved from http://nptel.ac.in/courses/120108005/module1/lecture1.pdf
- Yelebe Z.R., and Puyate Y.T., (2012) “Effect of Bioaugumentation on aerobic digestion of biodegradable organic waste”, J. Appl. Technol, Environ Sanit. 2(3)165-174.
Online Resources
- https://www.geo.lu.lv/fileadmin/user_upload/lu_portal/projekti/gzzf/videunilgtspejigaattistiba/Vid Z1000/16.LECTURE-Solid_waste_management.pdf
- http://www.indiawaterportal.org/topics/solid-waste
- Cogent Environmental Science (2016), 2: 1139434 http://dx.doi.org/10.1080/23311843.2016.1139434
- https://en.wikipedia.org/wiki/Biomedical_waste
- https://en.wikipedia.org/wiki/Industrial_waste
- Image Source : Google Image
1
Comments
Post a Comment