A Gap Analysis in Selected Asian Countries, 3R Knowledge Hub ...

A Gap Analysis in Selected Asian Countries, 3R Knowledge Hub ... A Gap Analysis in Selected Asian Countries, 3R Knowledge Hub ...

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54 3R Gap Analysis and Findings HEALTHCARE WASTE Healthcare waste management in India has been receiving greater attention due to recent regulations i.e. Biomedical Wastes Management & Handling Rules, 1998. The prevailing situation was analyzed, covering various issues like quantities and proportion of different constituents of wastes, handling, treatment and disposal methods in various healthcare units, and indicates that the waste generation rate varies between 0.5 and 2.0 kg/bed/day (Patil and Shekdar, 2001). It is also estimated that about 0.33 million tons of healthcare waste is generated in India every year. Solid waste from the hospital consists of bandages, linen and other infectious waste (30–35%), plastics (7–10%), disposable syringes (3–5%), glass (3–5%) and other general wastes including food (40–45%). Except a few places, wastes are collected in mixed form, transported and disposed of along with MSWs. At many places, authorities are failing to install appropriate systems for a variety of reasons, such as non-availability of appropriate technologies, inadequate financial resources and absence of professional training on waste management. Healthcare waste is a serious problem in India, where ragpickers get exposed through contaminated hospital garbage to recover the glass, paper, plastic and metal that they can sell for recycling. To protect them and others who could easily find and reuse contaminated needles and other medical supplies, a safe system of disposing of medical waste is urgently needed. Findings Healthcare waste technology market is seeing a steady influx of alternate technologies. There are already a number of autoclave, hydroclave and microwave technologies available. Centralized and shared waste treatment facilities are now being allowed within legislation, also because of NGO promotion. Centralized facilities allow not only for more state-of the art facilities to be installed, but also help in ensuring that these adhere to regulatory norms. Instead of resource strapped pollution control bodies (monitoring individual stacks in hospitals), centralized facilities reduce this to a few in the city. Economies of scale allow for more cost effective technologies and capacities, besides running in a scientific manner through trained staff. Considering that a small percentage of healthcare waste, consisting of mostly pathological wastes and body parts, needs to be incinerated, this can be carried out by sharing the many existing incinerators in a city. A zonal or centralized autoclave or microwave disinfecting unit can then take care of the rest of the waste. Healthcare waste management is not only a technical problem, but is also strongly influenced by economic conditions. On its own, enactment of legislation will not make it more efficient. Sustainable solutions can be achieved only by involving local bodies engaged in waste management and making sure they follow the principles of effective management. Healthcare waste should be subjected to disinfection and mutilation prior to reuse, recycling or disposal. Precautions have to be taken so that disposable items like needles, syringes, intravenous sets and other plastic items are not reused. Efforts have to be made for minimizing waste. An appropriate plan has to be evolved as per the prevailing conditions. Instead of incinerating their waste, hospitals should: • phase-out the use of PVC plastics and mercury products; • reduce, segregate and recycle as much waste as possible; • shred contaminated waste for volume reduction and avoid reuse, and then sterilize the material using high temperature steam or microwaving before disposal in dumpsites. E-WASTE The government, industry, users and NGOs have taken notice of the growing hazards of ewaste and reached a consensus that recycling and resource recovery has to be environmentally compatible. A national Waste Electrical and Electronic Equipment (WEEE) Task Force was formed in July 2004. Headed by the Chairman Central Pollution Control Board (CPCB), the Task Force consists of representatives from relevant Government Departments, Ministry of Information Technology, Regulatory Agencies (representatives of SPCBs), NGOs, Industry Associations, experts and producers.

The mandate of the National Task Force is to identify, plan and implement all issues related to e-waste in India. The National WEEE Task force has five thrust areas: Policy and Legislation, Baseline Study, Restructuring and Recycling, Extended Producer Responsibility and Awareness Building. The first comprehensive study to estimate the annual generation of e-waste in India is being undertaken by the National WEEE Taskforce. So far, the preliminary estimates suggest that total WEEE generation in India is approximately 146,000 tons per year. The top states in order of highest contribution to WEEE include Maharashtra, Andhra Pradesh, Tamil Nadu, Uttar Pradesh, West Bengal, Delhi, Karnataka, Gujarat, Madhya Pradesh and Punjab. The city wide ranking of largest WEEE generators is Mumbai, Delhi, Bangalore, Chennai, Kolkatta, Ahmedabad, Hyderabad, Pune, Surat and Nagpur. Approximately 30,000 computers become obsolete every year from the IT industry in Bangalore alone. The reason is an extremely high obsolescence rate of 30% per year. Almost 50% of the personal computers sold in India are products from secondary markets and are re-assembled on old components. The remaining market share is covered by multinational manufacturers (30%) and Indian brands (22%). Three categories of WEEE account for almost 90% of the generation, large household appliances (42.1%), information and communications technology equipment (33.9%) and consumer electronics (13.7%). The Government of India has reiterated its commitment to waste minimization and control of hazardous wastes, both nationally and internationally. The Basel Convention on the control of Transboundary Movement of Hazardous Wastes and Disposal was signed by India on 15 th March 1990, ratified and acceded in 1992. A ratification of this convention obliges India to address the problem of transboundary movement and disposal of dangerous hazardous wastes through international cooperation. As per the Basel Convention, India cannot export hazardous wastes listed in Annex VIII of the Convention. However, the convention agreement does not restrict the import of such wastes from countries that have not ratified the Basel Convention. It is through the orders of the Honorable Supreme Court that the import of such wastes is now banned in the country. The legal basis therefore is regulated in the Hazardous Waste Management and Handling Rules (1989/2000 amended and subsequently in 2003). This document also controls the import of hazardous waste from any part of the world into India. However, import of such waste may be allowed for processing or reuse as raw materials. There is no specific legislation pertaining to the management of e-waste so far. Findings Formal e-waste recyclers are in a nascent stage, with the first ones being established in Bangalore. Currently, the collection, dismantling and recovery are done entirely by a well-established network in the informal sector. Even though the sector creates substantial value addition, especially by collecting and repairing unused equipment, some recovery processes employed are extremely dangerous. Trade in e-waste, like that in other scrap, is dominated by the informal sector. The waste trade sector in India, known as a part of the informal sector, has a system that is highly organized with extensive coordination in an established network. However, e-waste recycling is undertaken in a very unscientific manner, impacting both health and environment. GAPS FOR IMPLEMENTATION OF 3R Worldwide experiences indicate that applying 3R is a lucrative way of tackling waste management issues. The first step in this exercise is an assessment of the technology options available for implementing 3R-based solutions. Proactive policies and relevant legislations emphasizing 3R-based solutions are vital to achieve a higher success rate form the next step. While recycling is considered as a technological ability, reduce and reuse is often considered management or policy oriented. In this context, the following sections present information on the technology and management aspects with focus on 3R. Chapter 3: Country Analysis 55

54<br />

<strong>3R</strong> <strong>Gap</strong> <strong>Analysis</strong> and F<strong>in</strong>d<strong>in</strong>gs<br />

HEALTHCARE WASTE<br />

Healthcare waste management <strong>in</strong> India has been<br />

receiv<strong>in</strong>g greater attention due to recent<br />

regulations i.e. Biomedical Wastes Management<br />

& Handl<strong>in</strong>g Rules, 1998. The prevail<strong>in</strong>g situation<br />

was analyzed, cover<strong>in</strong>g various issues like<br />

quantities and proportion of different<br />

constituents of wastes, handl<strong>in</strong>g, treatment and<br />

disposal methods <strong>in</strong> various healthcare units, and<br />

<strong>in</strong>dicates that the waste generation rate varies<br />

between 0.5 and 2.0 kg/bed/day (Patil and<br />

Shekdar, 2001). It is also estimated that about<br />

0.33 million tons of healthcare waste is generated<br />

<strong>in</strong> India every year. Solid waste from the hospital<br />

consists of bandages, l<strong>in</strong>en and other <strong>in</strong>fectious<br />

waste (30–35%), plastics (7–10%), disposable<br />

syr<strong>in</strong>ges (3–5%), glass (3–5%) and other general<br />

wastes <strong>in</strong>clud<strong>in</strong>g food (40–45%).<br />

Except a few places, wastes are collected <strong>in</strong> mixed<br />

form, transported and disposed of along with<br />

MSWs. At many places, authorities are fail<strong>in</strong>g to<br />

<strong>in</strong>stall appropriate systems for a variety of<br />

reasons, such as non-availability of appropriate<br />

technologies, <strong>in</strong>adequate f<strong>in</strong>ancial resources and<br />

absence of professional tra<strong>in</strong><strong>in</strong>g on waste<br />

management.<br />

Healthcare waste is a serious problem <strong>in</strong> India,<br />

where ragpickers get exposed through<br />

contam<strong>in</strong>ated hospital garbage to recover the<br />

glass, paper, plastic and metal that they can sell<br />

for recycl<strong>in</strong>g. To protect them and others who<br />

could easily f<strong>in</strong>d and reuse contam<strong>in</strong>ated needles<br />

and other medical supplies, a safe system of<br />

dispos<strong>in</strong>g of medical waste is urgently needed.<br />

F<strong>in</strong>d<strong>in</strong>gs<br />

Healthcare waste technology market is see<strong>in</strong>g a<br />

steady <strong>in</strong>flux of alternate technologies. There are<br />

already a number of autoclave, hydroclave and<br />

microwave technologies available. Centralized<br />

and shared waste treatment facilities are now<br />

be<strong>in</strong>g allowed with<strong>in</strong> legislation, also because of<br />

NGO promotion. Centralized facilities allow not<br />

only for more state-of the art facilities to be<br />

<strong>in</strong>stalled, but also help <strong>in</strong> ensur<strong>in</strong>g that these<br />

adhere to regulatory norms. Instead of resource<br />

strapped pollution control bodies (monitor<strong>in</strong>g<br />

<strong>in</strong>dividual stacks <strong>in</strong> hospitals), centralized<br />

facilities reduce this to a few <strong>in</strong> the city.<br />

Economies of scale allow for more cost effective<br />

technologies and capacities, besides runn<strong>in</strong>g <strong>in</strong> a<br />

scientific manner through tra<strong>in</strong>ed staff.<br />

Consider<strong>in</strong>g that a small percentage of<br />

healthcare waste, consist<strong>in</strong>g of mostly<br />

pathological wastes and body parts, needs to be<br />

<strong>in</strong>c<strong>in</strong>erated, this can be carried out by shar<strong>in</strong>g<br />

the many exist<strong>in</strong>g <strong>in</strong>c<strong>in</strong>erators <strong>in</strong> a city. A zonal<br />

or centralized autoclave or microwave<br />

dis<strong>in</strong>fect<strong>in</strong>g unit can then take care of the rest of<br />

the waste.<br />

Healthcare waste management is not only a<br />

technical problem, but is also strongly<br />

<strong>in</strong>fluenced by economic conditions. On its own,<br />

enactment of legislation will not make it more<br />

efficient. Susta<strong>in</strong>able solutions can be achieved<br />

only by <strong>in</strong>volv<strong>in</strong>g local bodies engaged <strong>in</strong> waste<br />

management and mak<strong>in</strong>g sure they follow the<br />

pr<strong>in</strong>ciples of effective management. Healthcare<br />

waste should be subjected to dis<strong>in</strong>fection and<br />

mutilation prior to reuse, recycl<strong>in</strong>g or disposal.<br />

Precautions have to be taken so that disposable<br />

items like needles, syr<strong>in</strong>ges, <strong>in</strong>travenous sets<br />

and other plastic items are not reused. Efforts<br />

have to be made for m<strong>in</strong>imiz<strong>in</strong>g waste. An<br />

appropriate plan has to be evolved as per the<br />

prevail<strong>in</strong>g conditions. Instead of <strong>in</strong>c<strong>in</strong>erat<strong>in</strong>g<br />

their waste, hospitals should:<br />

• phase-out the use of PVC plastics and<br />

mercury products;<br />

• reduce, segregate and recycle as much waste<br />

as possible;<br />

• shred contam<strong>in</strong>ated waste for volume<br />

reduction and avoid reuse, and then sterilize<br />

the material us<strong>in</strong>g high temperature steam or<br />

microwav<strong>in</strong>g before disposal <strong>in</strong> dumpsites.<br />

E-WASTE<br />

The government, <strong>in</strong>dustry, users and NGOs<br />

have taken notice of the grow<strong>in</strong>g hazards of ewaste<br />

and reached a consensus that recycl<strong>in</strong>g<br />

and resource recovery has to be environmentally<br />

compatible.<br />

A national Waste Electrical and Electronic<br />

Equipment (WEEE) Task Force was formed <strong>in</strong><br />

July 2004. Headed by the Chairman Central<br />

Pollution Control Board (CPCB), the Task Force<br />

consists of representatives from relevant<br />

Government Departments, M<strong>in</strong>istry of<br />

Information Technology, Regulatory Agencies<br />

(representatives of SPCBs), NGOs, Industry<br />

Associations, experts and producers.

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