This document summarizes a health risk assessment for rag pickers conducted in Pipali, India. It finds that:
1) Rag pickers are exposed to high concentrations of pathogens like Staphylococcus aureus through skin contact with waste, inhalation of aerosols, and hand-to-mouth transfer.
2) Risk analysis shows infection risks from S. aureus exceed internationally accepted safe levels through both skin wounds and oral ingestion.
3) While hand washing provides some reduction, barriers like gloves and masks are likely more effective at preventing initial skin contamination and subsequent infection through wounds or ingestion.
4) Rag pickers should be informed of risks and provided affordable protective equipment,
Listen to the untold story of Marjina - A Rag Picker. Her story will make you think twice before facing with any rag picker on a road-side. Rag pickers provides a great service to our city, but still our perspective on them is still the same. Listen and judge yourself..
This presentation focuses on a short history of bioterrorism, description, its advantages and disadvantages and organisms incorporated into weapons are also shown here.
Listen to the untold story of Marjina - A Rag Picker. Her story will make you think twice before facing with any rag picker on a road-side. Rag pickers provides a great service to our city, but still our perspective on them is still the same. Listen and judge yourself..
This presentation focuses on a short history of bioterrorism, description, its advantages and disadvantages and organisms incorporated into weapons are also shown here.
An adult male receives all his water from a municipal supply that is.pdfcallawaycorb73779
An adult male receives all his water from a municipal supply that is contaminated with
0.003mg/Lof tetrachloroethylene (PCE). Assume he takes a 15-minute shower every day. The
PCE concentration in the air is in equilibrium with the PCE in the water and thus can be
determined by Henry’s law from the concentration in the water. PCE has a unitless Henry’s
constant KH=1.4, which means Cair=Caq/KH. The dermal permeability constant of PCE is
6.17×10-5 m/min. (10 pts)
a. Calculate his total annual (ED=AT=1 yr) LADD due to exposures of drinking the water and
showering (dermal absorption + inhalation) with the water.
b. Which of the three modes of exposure results in the highest delivered dose?
Solution
There are generally three routes of exposure: dermal, oral and inhalation, as clear from the
question. Intake from these routes of exposure differ based upon the chemical and physical
properties of the toxicant as well as the permeability of the surface at the site of absorbtion, here,
lung, skin and the GI tract.
LADD (Lifetime Average Daily Dose) is obtained by adding up the AADD(Average Adsorbed
Daily Dose) for all the years of a person\'s life, namely:
->infant (1yr),
->child (1-6yrs),
->child (7-12 yrs),
->adolescents (13-18yrs),
->adults (19-70yrs)
AADD is obtained by adding adsorbed dose (AD) through all the 3 ways.
AD=Exposure x Adsorption Factor
Exposure = Concentration x Intake x Duration x Frequency
Body Weight
_____________________________________________________________________________
____
Another way to calculate LADD is:
LADD = (C x IR x ED)/(BW x LT) ;
where;
C = concentration of chemical
IR = intake rate
ED = exposure duration
BW = body weight
LT = lifetime (also AT)
(a) Total Annual LADD due to drinking water + showering
(1) Drinking water
C = 0.003 mg/L
IR = 2 L daily; for 1 year = 2*365 = 730 L
ED = AT = 1 year = 365 days
LT = 70 years = 25,550 days
BW = 70 kg
i.e, LADD = (0.003 * 730 * 1) / (70 *365)
= 8.57 x 10-5 mg/kg.day
(2) Similarly, for dermal absorption
For dermal adsorption,
Dosage, D = (C x P x SA x ET x CF) / (BW); where
D = Dose ( mg/kg day)
C = conc. of contaminant (mg/L)
P=Permeability coefficient (cm/hr)
SA = exposed body surface area (cm2); here 19400 cm2 (Standard value)
ET = Exposure time (hrs/day); here 0.25 hours /day
CF = conversion factor = 1 L/1000 cm3
BW = body weight = 70 kg
thus, D= (0.003*(6.15*10-5*10-2/60)*19400*0.25))/(1000*70)
=2.13*10-12 mg/kg.day.
However for 1 year, D = 7.776 * 10-10 mg/kg.day
Thus, total LADD = 8.57*10-5 + 7.776 * 10-10 = 8.57 * 10-5 mg/kg.day
(b)
Usually, studies show that of all the modes of exposure, ingestion or drinking the water will
deliver the highest dose.
Here, dosage due to air inhalation will be 8.57 * 10-5 / 1.4
= 6.121 * 10-5 mg/kg.day (as Cair = Caq/1.4)
Thus, comparing all the values, drinking the water will cause more dosage..
Slides for a lecture given at the University of Vienna postgraduate course on Toxicology/Science of Chemical Safety (Universitätslehrgang Toxikologie/Chemical Safety für Postgraduierte). See... http://www.meduniwien.ac.at/krebsforschung/research/research-units/chemical-safety-and-cancer-prevention/en/
Estimation of infectious risks in residential populations near a center pivot...LPE Learning Center
Full proceedings at: http://www.extension.org/72757 Manure wastewaters from dairy operations are commonly spray irrigated, thus there are concerns over downwind residential populations being exposed to airborne pathogens.In response, a quantitative microbial risk assessment (QMRA) was undertaken to estimate infectious risks from inhaling, then ingesting pathogens aerosolized during center pivot irrigation of dairy wastewaters. Four irrigation scenarios and associated pathogen emission rates from a 396 m long center pivot were developed based upon available information. The dispersion of bacterial pathogens (C. jejuni, E. coli O157:H7, non-O157, L. monocytogenes, and Salmonella spp.) was modeled using the U.S. EPA steady-state Gaussian plume model, AERMOD. Pathogen concentrations at downwind receptors were used to calculate infectious risks during one-time (1, 8, and 24 h) and multi-day (7 d at 1 h/d) exposure events using a Beta-Poisson dose-response model. This assessment considered risk of infection in adult non-immunocompromised residential populations that were 1 to 10 km from a center pivot that was spraying 5 to 20% dairy wastewater during day or night conditions.
Two field experiment were run at the farms of Omar AL-Mokhtar university, in order to knew the effect of some methods used to control tomato pests on soil arthropod systemic groups in organic cultivated tomato field such as (BT, algifol, methyl salicylate, neem oil), Results indicated that application of B. thuringensis and Algifol achieved the highest performance showing 100% reduction in mites and other soil arthropods systemic groups, and gave reduction 55.5 and 54.96% in both insect and total population of soil arthropods collected with pitfall traps. As far as Neemazone and Methyl salicylate increased the insect population with percentages 132.5 and 310% and total soil arthropods with 133.2% and 308.6% respectively and reduced the mites and the other arthropods population with 100%. Also results showed that the pesticides (avermectin, indoxacarb, & neemazone) increased the average number of the total soil arthropod population groups, and these pesticides showed selective effect, so that, it will be recommended that in order to preserve the beneficial predators, carnivorous and parasitoids these biological and selective pesticides in conventional tomato field should be applied.
According to the results obtained from this work, the changes in diversity and equitability and decrease or increase of percent population of soil arthropods groups were differed according to the soil arthropod groups, sampling period, applied plant protection products and system of agricultural.
The Senegalese grasshopper Oedaleus senegalensis (Krauss, 1877) is a serious agricultural pest in Senegal. The use of chemical pesticides on a large scale has raised concerns because of side effects on health and the environment. As an alternative to chemical control, a fungal strain of Metarhizium anisopliae (Metschnikoff, Sorokin) was isolated from the Senegalese grasshopper, and grown in agar culture medium. The effect on O. senegalensis was studied with an oil fungus formulation of 340 × 105 conidia/ml. Spraying took place in the field, and both nymphs and adults were infected with the fungus oil formulation. A total of 1.5 liter oil formulation of fungus was used for 1500 m2. Two methods were used to assess effectiveness: 1) we captured infected insects and fed them fresh grass daily in the laboratory and recorded time to death; 2) we counted insects in the field before and after application. In the field, the number of insects decreased significantly after the fungus treatment. In the laboratory, the lethal time at which 50% of the insects died varied between 8 to 9 days. The effectiveness of M. anisopliae in natural environment decreased with time.
Anti-Microbial allows for a Healthier Community & and many more benefits!!Nashville Fitness Supply
Anti-Microbial is easily applied between unit turns. Resulting in a healthier tenant, which leads to a working tenant.
Also can be applied in your Fitness Room, Offices, around the pool area which extends the life of the concrete and eliminates wet surfaces (less slip and fall) and mold.
An adult male receives all his water from a municipal supply that is.pdfcallawaycorb73779
An adult male receives all his water from a municipal supply that is contaminated with
0.003mg/Lof tetrachloroethylene (PCE). Assume he takes a 15-minute shower every day. The
PCE concentration in the air is in equilibrium with the PCE in the water and thus can be
determined by Henry’s law from the concentration in the water. PCE has a unitless Henry’s
constant KH=1.4, which means Cair=Caq/KH. The dermal permeability constant of PCE is
6.17×10-5 m/min. (10 pts)
a. Calculate his total annual (ED=AT=1 yr) LADD due to exposures of drinking the water and
showering (dermal absorption + inhalation) with the water.
b. Which of the three modes of exposure results in the highest delivered dose?
Solution
There are generally three routes of exposure: dermal, oral and inhalation, as clear from the
question. Intake from these routes of exposure differ based upon the chemical and physical
properties of the toxicant as well as the permeability of the surface at the site of absorbtion, here,
lung, skin and the GI tract.
LADD (Lifetime Average Daily Dose) is obtained by adding up the AADD(Average Adsorbed
Daily Dose) for all the years of a person\'s life, namely:
->infant (1yr),
->child (1-6yrs),
->child (7-12 yrs),
->adolescents (13-18yrs),
->adults (19-70yrs)
AADD is obtained by adding adsorbed dose (AD) through all the 3 ways.
AD=Exposure x Adsorption Factor
Exposure = Concentration x Intake x Duration x Frequency
Body Weight
_____________________________________________________________________________
____
Another way to calculate LADD is:
LADD = (C x IR x ED)/(BW x LT) ;
where;
C = concentration of chemical
IR = intake rate
ED = exposure duration
BW = body weight
LT = lifetime (also AT)
(a) Total Annual LADD due to drinking water + showering
(1) Drinking water
C = 0.003 mg/L
IR = 2 L daily; for 1 year = 2*365 = 730 L
ED = AT = 1 year = 365 days
LT = 70 years = 25,550 days
BW = 70 kg
i.e, LADD = (0.003 * 730 * 1) / (70 *365)
= 8.57 x 10-5 mg/kg.day
(2) Similarly, for dermal absorption
For dermal adsorption,
Dosage, D = (C x P x SA x ET x CF) / (BW); where
D = Dose ( mg/kg day)
C = conc. of contaminant (mg/L)
P=Permeability coefficient (cm/hr)
SA = exposed body surface area (cm2); here 19400 cm2 (Standard value)
ET = Exposure time (hrs/day); here 0.25 hours /day
CF = conversion factor = 1 L/1000 cm3
BW = body weight = 70 kg
thus, D= (0.003*(6.15*10-5*10-2/60)*19400*0.25))/(1000*70)
=2.13*10-12 mg/kg.day.
However for 1 year, D = 7.776 * 10-10 mg/kg.day
Thus, total LADD = 8.57*10-5 + 7.776 * 10-10 = 8.57 * 10-5 mg/kg.day
(b)
Usually, studies show that of all the modes of exposure, ingestion or drinking the water will
deliver the highest dose.
Here, dosage due to air inhalation will be 8.57 * 10-5 / 1.4
= 6.121 * 10-5 mg/kg.day (as Cair = Caq/1.4)
Thus, comparing all the values, drinking the water will cause more dosage..
Slides for a lecture given at the University of Vienna postgraduate course on Toxicology/Science of Chemical Safety (Universitätslehrgang Toxikologie/Chemical Safety für Postgraduierte). See... http://www.meduniwien.ac.at/krebsforschung/research/research-units/chemical-safety-and-cancer-prevention/en/
Estimation of infectious risks in residential populations near a center pivot...LPE Learning Center
Full proceedings at: http://www.extension.org/72757 Manure wastewaters from dairy operations are commonly spray irrigated, thus there are concerns over downwind residential populations being exposed to airborne pathogens.In response, a quantitative microbial risk assessment (QMRA) was undertaken to estimate infectious risks from inhaling, then ingesting pathogens aerosolized during center pivot irrigation of dairy wastewaters. Four irrigation scenarios and associated pathogen emission rates from a 396 m long center pivot were developed based upon available information. The dispersion of bacterial pathogens (C. jejuni, E. coli O157:H7, non-O157, L. monocytogenes, and Salmonella spp.) was modeled using the U.S. EPA steady-state Gaussian plume model, AERMOD. Pathogen concentrations at downwind receptors were used to calculate infectious risks during one-time (1, 8, and 24 h) and multi-day (7 d at 1 h/d) exposure events using a Beta-Poisson dose-response model. This assessment considered risk of infection in adult non-immunocompromised residential populations that were 1 to 10 km from a center pivot that was spraying 5 to 20% dairy wastewater during day or night conditions.
Two field experiment were run at the farms of Omar AL-Mokhtar university, in order to knew the effect of some methods used to control tomato pests on soil arthropod systemic groups in organic cultivated tomato field such as (BT, algifol, methyl salicylate, neem oil), Results indicated that application of B. thuringensis and Algifol achieved the highest performance showing 100% reduction in mites and other soil arthropods systemic groups, and gave reduction 55.5 and 54.96% in both insect and total population of soil arthropods collected with pitfall traps. As far as Neemazone and Methyl salicylate increased the insect population with percentages 132.5 and 310% and total soil arthropods with 133.2% and 308.6% respectively and reduced the mites and the other arthropods population with 100%. Also results showed that the pesticides (avermectin, indoxacarb, & neemazone) increased the average number of the total soil arthropod population groups, and these pesticides showed selective effect, so that, it will be recommended that in order to preserve the beneficial predators, carnivorous and parasitoids these biological and selective pesticides in conventional tomato field should be applied.
According to the results obtained from this work, the changes in diversity and equitability and decrease or increase of percent population of soil arthropods groups were differed according to the soil arthropod groups, sampling period, applied plant protection products and system of agricultural.
The Senegalese grasshopper Oedaleus senegalensis (Krauss, 1877) is a serious agricultural pest in Senegal. The use of chemical pesticides on a large scale has raised concerns because of side effects on health and the environment. As an alternative to chemical control, a fungal strain of Metarhizium anisopliae (Metschnikoff, Sorokin) was isolated from the Senegalese grasshopper, and grown in agar culture medium. The effect on O. senegalensis was studied with an oil fungus formulation of 340 × 105 conidia/ml. Spraying took place in the field, and both nymphs and adults were infected with the fungus oil formulation. A total of 1.5 liter oil formulation of fungus was used for 1500 m2. Two methods were used to assess effectiveness: 1) we captured infected insects and fed them fresh grass daily in the laboratory and recorded time to death; 2) we counted insects in the field before and after application. In the field, the number of insects decreased significantly after the fungus treatment. In the laboratory, the lethal time at which 50% of the insects died varied between 8 to 9 days. The effectiveness of M. anisopliae in natural environment decreased with time.
Anti-Microbial allows for a Healthier Community & and many more benefits!!Nashville Fitness Supply
Anti-Microbial is easily applied between unit turns. Resulting in a healthier tenant, which leads to a working tenant.
Also can be applied in your Fitness Room, Offices, around the pool area which extends the life of the concrete and eliminates wet surfaces (less slip and fall) and mold.
This session provides a comprehensive overview of the latest updates to the Uniform Administrative Requirements, Cost Principles, and Audit Requirements for Federal Awards (commonly known as the Uniform Guidance) outlined in the 2 CFR 200.
With a focus on the 2024 revisions issued by the Office of Management and Budget (OMB), participants will gain insight into the key changes affecting federal grant recipients. The session will delve into critical regulatory updates, providing attendees with the knowledge and tools necessary to navigate and comply with the evolving landscape of federal grant management.
Learning Objectives:
- Understand the rationale behind the 2024 updates to the Uniform Guidance outlined in 2 CFR 200, and their implications for federal grant recipients.
- Identify the key changes and revisions introduced by the Office of Management and Budget (OMB) in the 2024 edition of 2 CFR 200.
- Gain proficiency in applying the updated regulations to ensure compliance with federal grant requirements and avoid potential audit findings.
- Develop strategies for effectively implementing the new guidelines within the grant management processes of their respective organizations, fostering efficiency and accountability in federal grant administration.
ZGB - The Role of Generative AI in Government transformation.pdfSaeed Al Dhaheri
This keynote was presented during the the 7th edition of the UAE Hackathon 2024. It highlights the role of AI and Generative AI in addressing government transformation to achieve zero government bureaucracy
Jennifer Schaus and Associates hosts a complimentary webinar series on The FAR in 2024. Join the webinars on Wednesdays and Fridays at noon, eastern.
Recordings are on YouTube and the company website.
https://www.youtube.com/@jenniferschaus/videos
What is the point of small housing associations.pptxPaul Smith
Given the small scale of housing associations and their relative high cost per home what is the point of them and how do we justify their continued existance
Many ways to support street children.pptxSERUDS INDIA
By raising awareness, providing support, advocating for change, and offering assistance to children in need, individuals can play a crucial role in improving the lives of street children and helping them realize their full potential
Donate Us
https://serudsindia.org/how-individuals-can-support-street-children-in-india/
#donatefororphan, #donateforhomelesschildren, #childeducation, #ngochildeducation, #donateforeducation, #donationforchildeducation, #sponsorforpoorchild, #sponsororphanage #sponsororphanchild, #donation, #education, #charity, #educationforchild, #seruds, #kurnool, #joyhome
A process server is a authorized person for delivering legal documents, such as summons, complaints, subpoenas, and other court papers, to peoples involved in legal proceedings.
Presentation by Jared Jageler, David Adler, Noelia Duchovny, and Evan Herrnstadt, analysts in CBO’s Microeconomic Studies and Health Analysis Divisions, at the Association of Environmental and Resource Economists Summer Conference.
Russian anarchist and anti-war movement in the third year of full-scale warAntti Rautiainen
Anarchist group ANA Regensburg hosted my online-presentation on 16th of May 2024, in which I discussed tactics of anti-war activism in Russia, and reasons why the anti-war movement has not been able to make an impact to change the course of events yet. Cases of anarchists repressed for anti-war activities are presented, as well as strategies of support for political prisoners, and modest successes in supporting their struggles.
Thumbnail picture is by MediaZona, you may read their report on anti-war arson attacks in Russia here: https://en.zona.media/article/2022/10/13/burn-map
Links:
Autonomous Action
http://Avtonom.org
Anarchist Black Cross Moscow
http://Avtonom.org/abc
Solidarity Zone
https://t.me/solidarity_zone
Memorial
https://memopzk.org/, https://t.me/pzk_memorial
OVD-Info
https://en.ovdinfo.org/antiwar-ovd-info-guide
RosUznik
https://rosuznik.org/
Uznik Online
http://uznikonline.tilda.ws/
Russian Reader
https://therussianreader.com/
ABC Irkutsk
https://abc38.noblogs.org/
Send mail to prisoners from abroad:
http://Prisonmail.online
YouTube: https://youtu.be/c5nSOdU48O8
Spotify: https://podcasters.spotify.com/pod/show/libertarianlifecoach/episodes/Russian-anarchist-and-anti-war-movement-in-the-third-year-of-full-scale-war-e2k8ai4
Russian anarchist and anti-war movement in the third year of full-scale war
Wastepicker qmra final (1)
1. Health Risk Assessment for Rag Pickers
QMRA Solid Waste Group
Kelly Baker, Firew Lemma, Shrawan Singh
2. • Demographics
– Mix of men and
women
– Adults and Children
– Predominantly low
Socio economic
status
• End product results
in recyclables that
can be sold
9. Percentage Distribution of Microbial Indicators
Isolated from Saliva, Urine, Stool, and/or Nasal
Passages of Rag Pickers
0%
20%
40%
60%
80%
100%
Indicators/PathogensObserved
Rag Pickers
Control
10. Staphylococcus aereus
• Gram +
• Environmental ecology
– Resistant to inactivation via UV, desiccation, etc.
• Not always pathogenic
• Pathogenic forms possess virulence genes encoding toxins
that can adhere to cells and inactivate antibodies, enabling
the bacterium to colonize cell surfaces and resist
immunological clearance.
• Acute Disease pathology
– Skin boils
– Respiratory disease (sinusitis)
– Gastrointestinal disease via food poisoning
• Infection of 100,000 organisms sufficient to produce enough
endotoxin to cause food intoxication
• Antibiotic-resistant forms of pathogenic S. aureus (e.g.
MRSA) is a worldwide problem in clinical medicine.
12. Rag Picker Risk Framework
Microbial
Concentration
(cfu/g)
Volume of
waste per day
(g/day)
Total
concentration in
waste/day
(cfu/day)
Transfer efficiency by air to
mouth (TEHS) * Frequency
breaths/day (ƒHM=1)
Duration of 8-12
hours/day at site * 0.75 kg
waste collected/hour * 5
Decay rate
(e(-kt))
Infection
Infection
Infection
Dose-response
(DR =
dose/person)
CFUw/g * Waste collected/day * total volume* e(-kt) = CFU/day * AWC * PW * ƒOS * TEOS = Ds * DRS
= Ds * ƒHM * TEHM = DM * DRG
Dose ingested
hand-to-mouth
in 5 minutes (DO)
Dose inhaled
Dose transferred
object to skin in 5
minutes (DS)
Transfer efficiency
object to skin (TEOS)
Frequency contact
hand-to-mouth (ƒHM)
Transfer efficiency
hands - mouth (TEHM)
Area of hand and
arm contacting
waste (ACO)
= infection skin
= infection gastrointestinal
Probability of
wound (PW =
0.8)
Total area of
hand/arm with
open wound (AWC)
frequency contact object
and skin (ƒOS)
*set to 1 as constant
13. Concentration Equation
Microbial
Concentration
(cfu/g)
Volume of
waste per day
(g/day)
Total
concentration in
waste/day
(cfu/day)
Duration of 8-12
hours/day at site * 0.75 kg
waste collected/hour * 5
Decay rate
(e(-kt))
CFU/g * Waste collected/day * total volume handled per day * e(-kt)
= CFU/day
Where t = ƒ (t | hours at dump site)
CFU/g * 7.5 kg/day * 5 * e(-0.06*t) = CFU (Staphylococcus aereus)/day
14. Subcutaneous Exposure Dose via Fomite to Skin Wound
Total
concentration in
waste/day
(cfu/day)
CFU/day * AWC * 0.8* 1* TEOS = Ds (Dose through wound on skin)
Where AWC = 0.0203 cm2
(AHAND*0.5)+(AARM*0.25)
Dose transferred
object to skin in 5
minutes (DS)
Transfer efficiency
object to skin (TEOS)
Area of hand and
arm contacting
waste (ACO)
Probability of
wound (PW =
0.8)
Total area of
hand/arm with
open wound (AWC)
frequency contact object
and skin (ƒOS)
*set to 1 as constant
CFU/day * AWC * PW * ƒOS * TEOS = Ds (Dose through wound on skin)
Where AWC = AW
ACO
Microbial
Concentration
(cfu/g)
Volume of
waste per day
(g/day)
Duration of 8-12
hours/day at site * 0.75 kg
waste collected/hour * 5
Decay rate
(e(-kt))
15. Gastrointestinal Exposure Dose via Hand-to-Mouth
Total
concentration in
waste/day
(cfu/day)
Dose ingested
hand-to-mouth
in 5 minutes (DO)
Dose transferred
object to skin in 5
minutes (DS)
Transfer efficiency
object to skin (TEOS)
Area of hand and
arm contacting
waste (ACO)
Probability of
wound (PW =
0.8)
Total area of
hand/arm with
open wound (AWC)
frequency contact object
and skin (ƒOS)
*set to 1 as constant
Microbial
Concentration
(cfu/g)
Volume of
waste per day
(g/day)
Duration of 8-12
hours/day at site * 0.75 kg
waste collected/hour * 5
Decay rate
(e(-kt))
Frequency contact
hand-to-mouth (ƒHM)
Transfer efficiency
hands - mouth (TEHM)
Ds (Dose through wound on skin) = * 1 * TEHM = DO (Dose Oral)
Ds (Dose through wound on skin) = * ƒHM * TEHM = DO (Dose Oral)
16. Rag Picker Risk of Subcutaneous and
gastrointestinal infection
Microbial
Concentration
(cfu/g)
Volume of
waste per day
(g/day)
Total
concentration in
waste/day
(cfu/day)
Duration of 8-12
hours/day at site * 0.75 kg
waste collected/hour * 5
Decay rate
(e(-kt))
Infection
Infection
Dose-response
(DR =
dose/person)
Dose ingested
hand-to-mouth
in 5 minutes (DO)
Dose transferred
object to skin in 5
minutes (DS)
Transfer efficiency
object to skin (TEOS)
Frequency contact
hand-to-mouth (ƒHM)
Transfer efficiency
hands - mouth (TEHM)
Area of hand and
arm contacting
waste (ACO)
Probability of
wound (PW =
0.8)
Total area of
hand/arm with
open wound (AWC)
frequency contact object
and skin (ƒOS)
*set to 1 as constant
Ds (Dose through wound on skin) = * ƒ (DR | µ) = RS
(Risk of subcutaneous infection via skin)
Ds (Dose through wound on skin) = * ƒ (DR | µ) = RO
(Risk of gastrointestinal infection via mouth)
17. Assumptions
Parameters Value References
Hours of working 10 hr/day Ray et al., 2004
Waste Handling rate 0.75 kg/hr Ray et al., 2004
Total recyclables Handling 7.5 kg/day Ray et al., 2004
Total waste Handling 5 fold Group assumption
Microbial Decay constant 0.06 Perez-rodriguez, 2013
Size of wound 0.0203 cm2 Group decision
Area of hand and arm adult 4510 cm2 EPA, 2011 edi.
Proportion of arm exposed 0.25 Group assumption
Proportion of hand exposed 0.5 Group assumption
Probability of having a wound 0.8 Ray et al., 2004
Transfer efficiency - fomite to skin 0.67 cfu/cm2 Lopez, et al., 2013
Transfer efficiency – skin to mouth 0.34 cfu/cm2 Ryen et al., 2014
K (median Staph Dose Response from
normal distribution)
8.21*10-8 cfu/cm2 Rose and Hass, 1999
Efficacy of Hand washing with soap 0.99 Luby, 2006
21. Risk due to Staph Exposure in Wounds
1.0E-06
1.0E-05
1.0E-04
1.0E-03
1.0E-02
1.0E-01
1.0E+00RiskofInfection(%)
Considered Safe Limit
Wound Exposure
22. Risk due to Oral Ingestion
1.0E-06
1.0E-05
1.0E-04
1.0E-03
1.0E-02
1.0E-01
1.0E+00RiskofInfection(%)
Considered Safe Limit
Oral ingestion Exposure
23. Risk Mitigation and Policy
• What is the impact of various occupational
interventions on the risk of Staphylococcus
aereus infection among rag pickers by skin,
oral, and respiratory pathways?
– Hand washing or hand sanitizer
– Masks
– Appropriate clothing barriers - footwear and
gloves
• Which might be most effective?
24. Rag Picker Risk Framework
Microbial
Concentration
(cfu/g)
Volume of
waste per day
(g/day)
Total
concentration in
waste/day
(cfu/day)
Duration of 8-12
hours/day at site * 0.75 kg
waste collected/hour * 5
Decay rate
(e(-kt))
Infection
Infection
Dose-response
(DR =
dose/person)
Dose ingested
hand-to-mouth
in 5 minutes (DM)
Dose transferred
object to skin in 5
minutes (DS)
Transfer efficiency
object to skin (TEOS)
Frequency contact
hand-to-mouth (ƒHM)
Transfer efficiency
hands - mouth (TEHM)
Area of hand and
arm contacting
waste (ACO)
= hand washing interventions
= barrier interventions
Probability of
wound (PW =
0.8)
Total area of
hand/arm with
open wound (AWC)
frequency contact object
and skin (ƒOS)
*set to 1 as constant
25.
26. Risk due to Oral Ingestion After
Washing the Exposed Body Parts
1.0E-06
1.0E-05
1.0E-04
1.0E-03
1.0E-02
1.0E-01
1.0E+00RiskofInfection(%)
Considered Safe Limit
Oral ingestion Exposure
Oral ingestion Exposure after Hand
Washing
27. Conclusions - Intervention Impact
• Hand washing with soap: typically 99% effective
– Not likely to prevent infection of wound;
• Exposure of wound to contaminated fomite is immediate
• Could reduce overall contamination on hands if practiced
frequently
– Not effective at preventing oral infection; cfu of
Staphylococcus aereus deposited on hands is still
>100,000cfu/wound
• Barriers like gloves (Not analyzed)
– Act upstream of both exposure pathways by
preventing hand contamination
– % effective
28. Risk Communication
• Rag pickers need to be informed of their occupational
risk of exposure to high concentrations of hazardous
pathogens.
• Waste sites are so contaminated by some organisms
that follow-up hand washing may not be effective.
• Barriers, like the use of gloves (and masks) are far more
likely to prevent skin contamination that can lead to
bacterial entry into wounds and ingestion by mouth.
• Rag pickers need to be provided access to affordable
and comfortable gloves, shoes, and clothing to protect
themselves.