Get Permission George, Babu, Raj, and Mathew: Bio-medical waste management practices of personal protective equipments pre and post Covid -19: A cross-sectional study


Introduction

The combination of textile technology and medical sciences led to the emergence of a new field called medical textiles or healthcare textiles. They have contributed immensely towards healthcare hygiene and personal protection, especially in the last 2 years of the Covid-19 pandemic. Though many natural and synthetic materials are utilized, polypropylene and polyester are the most widely used for manufacturing Personal Protective Equipment (PPE), surgical gowns, and drapes.

During the Covid -19 pandemic, Central Pollution Control Board (CPCB) of India issued guidelines for collection and disposal of medical textile waste according to the biomedical waste (BMW) management rule 2016.1 This rule has been updated to promote disinfection and recycling of these waste products to the best possible extent.

Polypropylene and polyester, though biologically inert and non-toxic, when burned will produce water (H2O) and carbon dioxide (CO2) as major products and aliphatic and aromatic toxic hydrocarbons as minor products.2 Our aim was to find out whether medical textiles especially Personal Protective Equipment (PPE) were recycled adequately during Covid-19 pandemic. The stack emission sample data for 2019 and 2021were collected to find out the parameters of the fumes that are emitted into the atmosphere and the possibility of any environmental hazard.

Materials and Methods

National Institute for Transforming India (NITI AAYOG) has selected Kerala state as having the best health care system in the country during the Covid-19 pandemic (2020 –2021). Kerala state is the only large state in the country where the entire Bio Medical Waste (BMW) is disposed off at one facility: IMAGE. (Indian Medical Association Goes Eco-friendly). IMAGE also has a barcoding system that enables it to correctly segregate, transport, track and dispose the BMW of the entire state. Therefore we decided to take Kerala state as the representative sample of the entire country.

Waste segregation was done at the source into color-coded bags in which the red bag goes for recycling and the yellow bag goes for incineration (Figure 1). We collected the data on the monthly disposal pattern (recycling and incineration) of BMW from Jan 2017 to April 2022. IMAGE stringently follows the barcoding system mandated by the biomedical waste management rule 2016 and revised CPCB guidelines. The bar code is scanned at the collection area and disposal area. The code gives information on the bag color, supplier, distributor, territory, and unique identity of the bag. All bags are individually weighed and entered into the data bank along with the corresponding bar code. The data regarding disposal of the BMW and stack emission data was collected after obtaining consent for the study from the IMAGE general body meeting conducted in April 2022.

We divided data into 3 periods, pre-covid (Jan 2017 – to March 2020), covid lockdown (April 2020 – September 2020) & covid relaxation period (Oct 2020- April 2022). We recorded the BMW recycled and incinerated in the entire state during this period. The covid lockdown period was excluded from analysis because of a lack of clarity regarding BMW management and constant revision in the guidelines for covid-19 pandemic.

Through the Right to Information Act of the Indian Government, we got the data regarding new covid cases from March 2020 to April 2022. May 2021 showed the maximum number of Covid-19 cases. We correlated this data with the BMW disposal pattern during the pre-covid and covid relaxation time periods. 

Statistical Analysis

Data were analyzed in SPSS version 21. Student’sT-test and Pearson correlation test were used for statistical analysis.

Figure 1

Revised biomedical waste segregation guidelines 2021

https://s3-us-west-2.amazonaws.com/typeset-prod-media-server/4d9af428-61ef-4eb6-85ca-456daa3b6c33image1.png

.

Figure 2

Covid relaxation period pattern of recycling, incineration and new cases

https://s3-us-west-2.amazonaws.com/typeset-prod-media-server/4d9af428-61ef-4eb6-85ca-456daa3b6c33image2.png
Table 1

Pre Covid period waste generation

Month

2017

2018

2019

Container

Red (In tons)

Yellow (In tons)

Red (In tons)

Yellow (In tons)

Red (In tons)

Yellow (In tons)

January- March

941.989

1402.395

1032.533

1723.234

924.557

1794.178

April-June

1031.96

1597.826

1076.790

1689.164

1048.354

1692.266

July-September

1077.72

1702.727

1151.004

1822.996

1213.068

1789.455

October-December

1058.06

1710.309

1116.182

1860.941

1227.655

1837.323

Total

4109.75

6413.257

4376.509

7096.335

4413.634

7113.222

Table 2

Covid relaxation period waste disposal and new cases

Month

Recycled(In tons)

Incinerated(In tons)

Covid New Cases

October-December 2020

1851.746

1799.958

564827

January-March2021

1594.242

3181.656

363651

April-June 2021

1622.465

3237.920

1799581

July-September 2021

1653.129

3299.176

1756693

October-December 2021

1621.350

3235.754

566319

January-April 2022

1828.055

3847.676

1294551

Total

10170.987

18602.140

6345622

Table 3

May 2021Covid waste

State

Tons /Day

No: CBWTF

Andhra

9.99

11

Bihar

1.06

4

Delhi

18.79

2

Gujarat

21.98

20

Haryana

13.11

11

Karnataka

16.91

26

Kerala

23.71

1

Maharashtra

19.02

29

Odisha

6.65

5

Tamil Nadu

13.57

8

Uttarpradesh

15.91

18

Table 4

2019 stack emission data

May-19

Oct-19

Nov-19

Dec-19

No:

Parameteres

Unit

5 incinerators

5 incinerators

5 incinerators

5 incinerators

1

Temperature

°C

62.4

71.2

71.4

75.25

2

Velocity of Gas

m/sec

5.9

6.14

6.132

5.89

3

Volume of Gas

Nm³/Hr

5332.2

5413

5961

5123.75

4

Particulate Matter

mg/Nm³

35.14

34.26

36.86

36.075

5

Hydrochloric Acid

mg/Nm³

6.59

6.52

6.52

6.92

6

Oxides of Nitrogen

mg/Nm³

19.26

19.58

20.88

20.725

7

Volatile organics

mg/Nm³

below detecton

below detection

below detecton

below detection

8

Combustion Efficiency

%

99.38

99.52

99.5

99.48

Table 5

2021 Stack emission data

Feb-21

May-21

Sep-21

Dec-21

No

Parameters

unit

4incinerators

3 incinerators

5 incinerators

6 incinerators

1

Particulate Matter

mg/Nm³

23.6

18.06

18.38

22.38

2

Hydrochloric Acid

mg/Nm³

2.7

2.23

3.07

4.39

3

Oxides of Nitrogen

mg/Nm³

13.15

13.8

18.54

32.51

4

Volatile organics

mg/Nm³

below detection

below detection

below detection

below detection

5

Combustion efficiency

%

99.65

99.3

99.5

99.61

Results 

During the three pre-covid years, Kerala incinerated 20622 tons of BMW, with an average of 572 tons every month and recycled 12899 tons with an average of 358 tons per month. The ratio of recycling to incineration was1:1.5 and showed a significant difference (p-value<0.05). In the Pre-Covid times, incineration was considerably more when compared to recycling of BMW. The total amount of BMW incinerated and recycled from January 2017 to April 2022 is shown Table 1, Table 2.

During covid relaxation period, the total BMW burnt was 18602 tons at a monthly average of 979 tons. This was a two fold increase in the incineration of BMW from the pre-covid situation and it was significant (p value<0.0001). This was equivalent to almost 90% of the total waste incinerated in 3 years during the pre-covid period. At the same time, total BMW recycled during the covid relaxation time was 10170 tons at a monthly average of 535 tons. The recycling increased significantly during covid relaxation when compared to the pre-covid times.(p-value- 0.05). However, the incineration to recycling ratio during pre-covid period was significantly less when compared to that of covid relaxation time period (p value<0.001). This suggests that, although there was a significant rise in incineration during the Covid times, the amount of BMW recycled was more or less constant suggesting that recycling did not increase significantly as expected.

Also, the increase in incineration and recycling during the covid relaxation period was not directly proportional to the fluctuation in the new cases reported (Table 2 and Figure 2). May 2021 also showed the highest number of new cases reported. From December 2020 when the new cases increased, the incineration increased but the recycling did not increase. Similarly, during the omicron wave that started in December 2021, the incineration numbers remained steady while recycling numbers came down. Though there was a substantial increase in incineration, it did not follow the same trend with respect to new cases (correlation coefficient r-value 0.15, p 0.98). Kerala state had produced the maximum Covid 19 BMW in May 2021 (Table 3) ie, 23.71 tons/ day (11% of the total covid waste of India). While in the year 2021 the total biomedical waste incinerated was 12954 tons (35.5 tons per day) and recycled was 6491tons (17.7tons/day). This increase is seen in the amount of incineration and not in recycling. This data shows that proper recycling was not carried out during the covid 19 pandemic.

The stack emission sampling data regarding the emission of any toxic fumes from incinerators were collected in 2019 and 2021. (Table 4, Table 5). Hydrochloric acid, oxides of nitrogen, and volatile organic compounds were within normal limits and did not show any change during the pre-covid and covid relaxation period. Five incinerators were functional in 2019. But, May 2021 showed only 3 functional incinerators. Four more new incinerators were added on by end of December 2021 with a stack diameter 0.90m.

Discussion 

India has the second-largest population in the world. Kerala state is the the 13th largest state in the country contributing to 2.6 percent of the Indian population. Kerala state had implemented a triple lock containment strategy which was found to be a very successful model in fighting Covid 19 pandemic.3 The state treated 65,41,728 new patients from January 2020 to April 2022. Strategies and challenges in Kerala’s response to the initial phase of the Covid-19 pandemic were also well appreciated,4 though the inappropriate reporting of the mortality rate was criticised by Karthik Natashekara through Benford’s law analysis.5

Biomedical waste management of the entire Kerala state is done by a non-government organisation named IMAGE. There are 13,057establishments in the state which includes 911 government establishments and 12095 private establishments in addition to old-age homes, dialysis centers, blood banks, Ayush institutions, and palliative clinics. This makes a bed strength of 93,266 and all these are registered with and managed by IMAGE. All the BMW is collected every day from all hospitals and disposed off within 24 hours. All waste is collected using color-coded and bar-coded bags with a unique identification number that can trace the BMW back from the disposal area to its origin. All the yellow bags go for incineration after weighing but without opening, while all red bags are weighed, opened autoclaved shredded compressed, and then sent for recycling. Therefore proper segregation is needed for ideal disposal especially to avoid plastic or PPE getting into incineration.6

Since 11th March 2020, when WHO declared the outbreak of Covid-19 as a pandemic, there was an increase in the demand and production of PPE all over the world. According to Market reports 2019: WHO 2020 has indicated a monthly increase of 40% in the production of PPE. In India, there are 198 Common Biomedical Waste Treatment Facilities (CBWTF) with an installed incineration capacity of 782 tons per day, with an additional capacity of 72 tons per day. Therefore, we decided to study the disposal pattern of this synthetic waste by a single CBWTF- IMAGE in the state of Kerala, with the highest production of waste in the country (Table 3), and possible environmental hazards that could arise as a result of it.7

V. Purohit et al has studied the various by-products of burning Polypropylene and polyester which are the main materials used for the production of PPE, in various environments6. Water and carbon dioxide are the major by-products and aliphatic and aromatic hydrocarbons are the minor by-products. When incinerated at more than 1100 degrees centigrade these hydrocarbons are not produced at all. But a large amount of incineration of PPE could lead to large volumes of Carbon dioxide being released into the atmosphere, contributing to an increase in global warming. Similarly, oxides of sulfur and nitrogen produced by BMW other than PPE, can also lead to smog formation.

Parteek Singh Thind et al has mentioned the compromising situation of India’s biomedical waste incineration units and associated carcinogenic and no carcinogenic emissions during Covid-19 initial phase in Delhi, Haryana, Rajasthan, Madhya Pradesh, Maharashtra, Mizoram, and Uttarakhand. Overview of the treatment of infectious and sharp waste from health care facilities by WHO 2019 also suggests only 28%hospitals in India segregate properly and 40% dispose of according to CPCB rules and regulations. Parteek et al has also recommended increasing the number of incinerators and looking for alternate technology for disposing of BMW waste.6

During the pre-Covid period, IMAGE has 5 incinerators, including one 24 hours rotary incinerator (Thermax, Alpha, Ensys, Alfa Thermax & Rotary) with a stack diameter of 0.60m to take care of the BMW. There was a fluctuation in the amount incinerated and recycled every month. But the wastes recycled showed a direct relation to incineration (1:1.5, p-value<0.05).

During the pre-Covid years, the CPCB had not provided adequate guidelines for disposing of gowns and drapes made of polypropylene. The practice was to segregate PPE into yellow BMW bags which was then incinerated. During the Covid period, Polypropylene-based sterile disposable gowns and surgical drapes were widely used instead of linen. We can notice that this practice of segregation into yellow bags continued into the Covid pandemic years. This was most evident during the relaxation months (Figure 2) where there was a significant increase in incineration but no proportionate increase in recycling (p value<0.0001).

In 2021 two spikes were noticed in the covid -19 case burden. The quantum of incineration of BMW increased but did not follow the same pattern of covid-19 case rise (correlation coefficient r-value 0.15, p 0.98). The difference between incineration and recycling was doubled when compared to the pre-covid years. This suggests that the additionally used disposable kits during these spikes of new cases were mostly incinerated rather than recycled (Figure 2).

The study from 7 north Indian states suggests that a Covid infected patient generates approximately 3.41 kg/d of BMW and the major proportion were PPE. Their study also showed Cadmium emissions from incinerating these wastes and were fatal for adults and children. CPCB in its revisions of the rules during the Covid-19 pandemic has focused on giving more importance to recycling after the disinfection of these PPE rather than incineration. IMAGE also revised its segregation rules accordingly (Figure 1).

Our study shows a similar finding to that of Parteek et al. about the forecasted burden on incineration in phase 2 and the recycling being inadequately utilised. IMAGE’s burden in this incinerated BMW is obvious from the data showing the addition of 0.90m stack diameter New parisudh incinerator, New Alpha incinerator, (0.375m stack diameter), 0.9m stack diameter Old Parisudh and a new Rotary incinerator. We did study the stack emission sampling data particulate matter, HCL, Oxides of Nitrogen, Volatile organic compounds, and combustion efficiency. There was no change when pre-Covid and Covid pandemic data were compared for the above parameter. The oxides of nitrogen has shown an increasing trend but was within the CPCB standards. But the large quantity emitted can have environmental effects like global warming.

From our study, it is evident that Kerala although being compliant with CPCB rules, has to be a little more vigilant when coming to the safe and efficient disposal of PPE especially when recycling of waste is concerned. Though IMAGE has issued guidelines regarding disposal of PPE in red coloured bags the reason for non-compliance has to be addressed. Awareness on safe segregation at source so that we remain eco-friendly has to be provided. All manufacturers of PPE should clearly mention that their product has to be strictly recycled by colour coding for segregation at source into red bag.

Source of Funding

None.

Conflict of Interest

None.

Acknowledgments

We like to acknowledge Dr Sangeetha Jithin and Dr Pramod Thomas of Community medicine department of Believers Church Medical College, Interns 2016 batch, Dr Sharaffudeen (IMAGE Secretary) and Mr Manoj Benjamin for collecting and processing the data.

References

1 

Central Pollution Control Board, Ministry of environment, forest and climate change, Government of India. Biomedical Waste Ruleshttps://cpcb.nic.in/bio-medical-waste-rules/.DOA:20/08/2022

2 

R Chandra S Sinha India Fighting COVID-19: Experiences and Lessons Learned From the Successful Kerala and Bhilwara ModelsDisaster Med Public Health Prep20211510.1017/dmp.2021.115

3 

K C Prajitha A Rahul S Chintha G Soumya Maheswari Suresh ANK Kesavan Nair Strategies and challenges in Kerala's response to the initial phase of COVID-19 pandemic: a qualitative descriptive studyBMJ Open2009117e05141010.1136/bmjopen-2021-051410

4 

K Natashekara COVID-19 cases in India and Kerala: a Benford’s law analysisJ Public Health (Oxf)202112J Public Health

5 

PS Thind A Sareen D Deep S Singh S John Compromising situation of India's bio-medical waste incineration units during pandemic outbreak of COVID-19: Associated environmental-health impacts and mitigation measuresEnviron Pollut202127611662110.1016/j.envpol.2021.116621

6 

V Purohit R A Polypropylene: A Literature Review of the Thermal Decomposition Products and Toxicity19887

7 

Central Pollution Control Board, Ministry of environment, forest and climate change, Government of India. Common HW Incinerators, Annexure -I.cpcb.nic.in/common-HW-incinerators-annexure/.



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Received : 20-04-2023

Accepted : 15-05-2023


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https://doi.org/10.18231/j.jpmhh.2023.004


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