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PRESENTATION ON:
PESTICIDE HAZARD ASSESSMENT
PEST AND PESTICIDE SURVEY AND SURVELLIANCE
FIELD MONITORING, SAMPLING AND BIOASSAY
Presenters:
Purushottam Dhodary (29)
Rahul KC (30)
Ashmita Khanal (31)
Ram Dhan Tharu (32)
Renu Ojha (33)
Sabina Tiwari (34)
Sachin Bhattarai (35)
PESTICIDES HAZARD
ASSESSMENT
• Pest : Organisms dangerous to cultivated plants
and animals. (insects, fungi, herbs, nematodes
etc.)
• Pesticides: Any substance used for killing pests.
• Insects, rodents, and humans have similar nervous,
circulatory, and respiratory systems, so pesticides can
affect people too!
• Health effects -short-or long-term
• Physical and chemical risks -explosive and
combustible
HAZARD=TOXICITY X EXPOSURE
Risk;the potential
for injury
The capacity of
a pesticide to
cause injury
The risk of a
pesticide
contacting or
entering the
body
HAZARD
•Lower toxicity = Less hazard
•Higher exposure = Greater hazard
•Lower exposure = Less hazard
HAZARD ASSESSMENT ?
• New pesticides must be evaluated before they
can enter the market.
• Existing pesticides must be re-evaluated
periodically to ensure that they continue to meet
the appropriate safety standard.
• Ecological risk assessment
• Human health risk assessment
• Assessing pesticide cumulative risk
• Models, databases, and guidelines
ECOLOGICAL RISK ASSESSMENT
• Planning and scoping process
Phase 1 - problem formulation
information is gathered to determine what plants and animals
are at risk and need to be protected.
Phase 2 - analysis
This is the determination of what plants and animals are
exposed and to what degree they are exposed, and whether or
not that level of exposure is likely to cause harmful ecological
effects.
Phase 3 - risk characterization
Risk characterization includes two major components: risk
estimation and risk description. "risk estimation" combines
exposure profiles (i.e., the findings of exposure
characterization) and effects from exposure. "risk
description" provides information important for interpreting
the risk results and identifies a level for harmful effects on
the plants and animals of concern.
HUMAN HEALTH RISK ASSESSMENT
A human health risk assessment is the process to
estimate the nature and probability of adverse health
effects in humans who may be exposed to chemicals in
contaminated environmental media, now or in the future.
human health risk assessments address questions such
as:
• What types of health problems are caused by
pesticides in the environment?
• What is the chance that people will experience
problems when exposed to different levels of
pesticides?
• Is there a low level below which some chemicals
don’t pose a human health risk?
• What pesticides are people exposed to and for how
long?
ASSESSING PESTICIDE CUMULATIVE RISK
This new assessment is called a cumulative risk
assessment and is designed to evaluate the risk of a
common toxic effect associated with concurrent exposure
by all relevant pathways and routes of exposure to a
group of chemicals that share a common mechanism of
toxicity.
MODELS, DATABASES, AND GUIDELINES
• The risk assessment process depends on having
appropriate data and using well tested models
HEALTH IMPACTS
Chronic impacts
• Increased risk of cancer
• Neurological impairment
• Developmental effects
• Reproductive effects
• Organ damage
• Intrusion with the human hormone system
Acute Impacts:
Eyes : tearing , irritation, conjunctivitis
Skin: rash ,blistering, burns, sweating ,contact
dermatitis, jaundice
Nervous system: headache dizziness, mood
disturbances, depression, stupor, muscle twitching, lack
of coordination, seizures, paralysis, loss of
consciousness, coma
Respiratory system :throat pain, rhinorrhoea, cough,
pulmonary oedema, difficult in breathing, respiratory
failure
Cardiovascular system: cardiac arrhythmias
PEST SURVEY
• Survey is a sampling or partial collection of facts,
figures or opinions taken and used to approximate or
indicate what a complete collection and analysis
might reveal.
• Pest survey activities involve sampling of plants for
various insects and pest, trapping and identifying
insects, and estimating insects populations.
• It is conducted to study the abundance of a pest
species.
TYPES OF SURVEY
Roving survey
• Assessment of pest population /damage from
randomly selected spots representing larger area.
• Larger area surveyed in short period
• Provides information on pest level over large area
Fixed plot survey
Assessment of pest population /damage from a
fixed plot selected in a field. The data on pest
population/damage recorded periodic from
sowing till harvest.
PEST SURVEILLANCE
• Pest surveillance refers to the constant watch on the
population dynamics of pests, its incidence and
damage on each crop at fixed intervals to forewarn the
farmers to take up timely crop protection measures
• Pest surveillance is necessary for exotics pest
eradication, market access, improved pest
management, pest status information
Basic components of pest
surveillance
Determination of-
• The level of incidence of the pest species
• The loss caused by the incidence
• The economics benefits, the control will provide
Objectives of pest surveillance
• To know existing and new pest species
• To assess pest population and damage at different
growth stage of crop
• To study the influence of weather parameters on pest
• To study changing pest status
• To assess natural enemies and their influence on pests
• To assess effects of new cropping pattern and varieties
on pest
PEST MONITORING
• Process of regularly observing measuring and recording conditions within a given area.
• Is an essential tool for pest management programs.
• Information gathered during monitoring includes:
Pest populations and infestation levels
Weather
Crop development and soil conditions
Population of both beneficial organisms
OBJECTIVES OF PEST MONITORING
• Predict and evaluate potential key pest problems and non-target effects
• Provides info for choosing and timing appropriate control actions
• Evaluates effectiveness of management practices
• Establishes a pest history for the specified area
BENEFITS OF MONITORING
• Greater awareness of pest activity, including changes in pest
populations.
• Up-to-date information on the health of your plants.
• Data that can be used to compare pest outbreaks from season to
season.
• Early detection of pest problems, resulting in the availability of
more management options.
SAMPLING TECHNIQUES
• Sampling technique is important to ensure a representative portion of the
crop has been monitored since pest activity is often patchy.
• Sampling parameters(e.g. number of samples per padlock and number of
leaves per sample) helps sampling consistency. sampling technique
includes:-
• Sample size
• Sample number
• Depend on crop type
• Crop age
• Padlock size
SAMPLING TYPES
1. ABSOLUTE SAMPLING-
• To count all the pests occurring in a plot
• Pests per spatial area
• Direct observation/count of pests: easier with static organisms
• Total census of pests within a given area
2. RELATIVE SAMPLING-
• To measure pest in terms of some values which can be compared over time and space e.g.
light trap catch, pheromone trap
• Pests per sampling effort i.e. sweeps with a sweep net
• Insects/spores per passive or active trap
• Partial census: sampling method is not 100% fool proof
• Relative measures can be transformed in to absolute measures
• This is often the basis for pest management thresholds
SAMPLING METHODS
BETA SHEET:-
Main tool used to sample row crops for pests and beneficial insects.
Beta sheets are particularly effective or sampling caterpillars, bugs, aphids
and mites.
A standard beat sheet is made from yellow or white taroaulin material with
heavy dowel on each end.
Beta sheets are generally between 1.3-1.5 m wide by 1.5-2.0 m deep (the
larger dimension are preferred for taller crops). the extra width on each side
catches insects thrown out sideways when sampling and the sheets depth
allow it to be draped over the adjacent plant row. this prevents insect being
escape through this row.
Other various sampling techniques can be used to quantify pest
populations in the field, they are:-
• In situ counts- visual observation on number of insects on plant canopy(either entire plot or randomly
selected plot)
• Knock down- collecting insect from an area by removing from crop and (sudden trap)counting
• Suction sampling- it is quick and relatively easy way to sample for mirids. its main drawback are
unacceptably low sampling efficiency, a propensity to suck up flowers and bees, noisy operation, high
purchase cost of the suction machine.
• Netting- use of sweep net for hoppers
• Narcotized collection- quick moving insects anaesthetised and counting
• Trapping- used to sample mobile insects. left out in the field for a period of time, then the number of
insects is counted.
• Pan trap: blue pan traps for aphids
• Pheromone trap: species specific
• Sticky trap: sucking insect
• Bait trap: Shoot fly and other flies
• Emergence trap: for soil insects
• Light traps – moths, mosquitoes, beetles
• STAGES OF SAMPLING
Usually most injurious stage counted but depends on the type of crop,
insects, history of insects, influences of biotic and abiotic factors on pest
population and insect nature of a damage.
• SAMPLE SIZE
Sample size differ with nature of pest and crop but large sample size gives
accurate result.
Sample size will depend on crop type, age and padlock size, and is often in
between the ideal number and location of samples and what is practically
possible.
Sample size should be enough to provide good field representation or
coverage
DECISION MAKING
• Decision regarding when to start control measure
depends on the population or damage assessed from
the crop.
• The pest population is compared to economic
threshold level and economic injury level.
• When pest level crosses ETL, control measure has to
be taken to prevent pest from ETL.
BIOASSAY
• A bioassay involves use of a biological organism to test for chemical toxicity.
• It involves the use of live animal or plant(in vivo) or tissue or cell(in vitro)to
determine the biological activity of the substance, such as a hormone or drugs.
• Bioassay are typically conducted to measure the effects of a substance on a
living organism, such as a hormone or drug.
PROPERTIES OF GOOD BIOASSAY:-
• Reproducibility (the “litmus test” of science)
• Results easily observed and measured
• Relatively low cost
• Preferably of short duration (less opportunity for confounding factors); more
replication
• Linear dose-response
PURPOSE OF BIOASSAY
• Measurements of the pharmacological activity of new or chemically
undefined substances.
• Investigation of the function of endogenous mediators.
• Determination of the side-effect profile, including the degree of the drug
toxicity.
• Measurement of the concentration of known substances(alternatives to
the use of the whole animals have made this use obsolete).
• Assessing the amount of pollutants being released by a particular source,
such as wastewater or urban runoff.
• Determining the specificity of certain enzymes to certain substrates.
THANK YOU VERY MUCH

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Pesticide Hazard Assessment

  • 1. PRESENTATION ON: PESTICIDE HAZARD ASSESSMENT PEST AND PESTICIDE SURVEY AND SURVELLIANCE FIELD MONITORING, SAMPLING AND BIOASSAY Presenters: Purushottam Dhodary (29) Rahul KC (30) Ashmita Khanal (31) Ram Dhan Tharu (32) Renu Ojha (33) Sabina Tiwari (34) Sachin Bhattarai (35)
  • 3. • Pest : Organisms dangerous to cultivated plants and animals. (insects, fungi, herbs, nematodes etc.) • Pesticides: Any substance used for killing pests.
  • 4. • Insects, rodents, and humans have similar nervous, circulatory, and respiratory systems, so pesticides can affect people too! • Health effects -short-or long-term • Physical and chemical risks -explosive and combustible
  • 5. HAZARD=TOXICITY X EXPOSURE Risk;the potential for injury The capacity of a pesticide to cause injury The risk of a pesticide contacting or entering the body
  • 6. HAZARD •Lower toxicity = Less hazard •Higher exposure = Greater hazard •Lower exposure = Less hazard
  • 7. HAZARD ASSESSMENT ? • New pesticides must be evaluated before they can enter the market. • Existing pesticides must be re-evaluated periodically to ensure that they continue to meet the appropriate safety standard.
  • 8. • Ecological risk assessment • Human health risk assessment • Assessing pesticide cumulative risk • Models, databases, and guidelines
  • 9. ECOLOGICAL RISK ASSESSMENT • Planning and scoping process Phase 1 - problem formulation information is gathered to determine what plants and animals are at risk and need to be protected. Phase 2 - analysis This is the determination of what plants and animals are exposed and to what degree they are exposed, and whether or not that level of exposure is likely to cause harmful ecological effects.
  • 10. Phase 3 - risk characterization Risk characterization includes two major components: risk estimation and risk description. "risk estimation" combines exposure profiles (i.e., the findings of exposure characterization) and effects from exposure. "risk description" provides information important for interpreting the risk results and identifies a level for harmful effects on the plants and animals of concern.
  • 11. HUMAN HEALTH RISK ASSESSMENT A human health risk assessment is the process to estimate the nature and probability of adverse health effects in humans who may be exposed to chemicals in contaminated environmental media, now or in the future. human health risk assessments address questions such as:
  • 12. • What types of health problems are caused by pesticides in the environment? • What is the chance that people will experience problems when exposed to different levels of pesticides? • Is there a low level below which some chemicals don’t pose a human health risk? • What pesticides are people exposed to and for how long?
  • 13. ASSESSING PESTICIDE CUMULATIVE RISK This new assessment is called a cumulative risk assessment and is designed to evaluate the risk of a common toxic effect associated with concurrent exposure by all relevant pathways and routes of exposure to a group of chemicals that share a common mechanism of toxicity.
  • 14. MODELS, DATABASES, AND GUIDELINES • The risk assessment process depends on having appropriate data and using well tested models
  • 15. HEALTH IMPACTS Chronic impacts • Increased risk of cancer • Neurological impairment • Developmental effects • Reproductive effects • Organ damage • Intrusion with the human hormone system
  • 16. Acute Impacts: Eyes : tearing , irritation, conjunctivitis Skin: rash ,blistering, burns, sweating ,contact dermatitis, jaundice Nervous system: headache dizziness, mood disturbances, depression, stupor, muscle twitching, lack of coordination, seizures, paralysis, loss of consciousness, coma Respiratory system :throat pain, rhinorrhoea, cough, pulmonary oedema, difficult in breathing, respiratory failure Cardiovascular system: cardiac arrhythmias
  • 17. PEST SURVEY • Survey is a sampling or partial collection of facts, figures or opinions taken and used to approximate or indicate what a complete collection and analysis might reveal. • Pest survey activities involve sampling of plants for various insects and pest, trapping and identifying insects, and estimating insects populations. • It is conducted to study the abundance of a pest species.
  • 18. TYPES OF SURVEY Roving survey • Assessment of pest population /damage from randomly selected spots representing larger area. • Larger area surveyed in short period • Provides information on pest level over large area
  • 19. Fixed plot survey Assessment of pest population /damage from a fixed plot selected in a field. The data on pest population/damage recorded periodic from sowing till harvest.
  • 20. PEST SURVEILLANCE • Pest surveillance refers to the constant watch on the population dynamics of pests, its incidence and damage on each crop at fixed intervals to forewarn the farmers to take up timely crop protection measures • Pest surveillance is necessary for exotics pest eradication, market access, improved pest management, pest status information
  • 21. Basic components of pest surveillance Determination of- • The level of incidence of the pest species • The loss caused by the incidence • The economics benefits, the control will provide
  • 22. Objectives of pest surveillance • To know existing and new pest species • To assess pest population and damage at different growth stage of crop • To study the influence of weather parameters on pest • To study changing pest status • To assess natural enemies and their influence on pests • To assess effects of new cropping pattern and varieties on pest
  • 23. PEST MONITORING • Process of regularly observing measuring and recording conditions within a given area. • Is an essential tool for pest management programs. • Information gathered during monitoring includes: Pest populations and infestation levels Weather Crop development and soil conditions Population of both beneficial organisms
  • 24. OBJECTIVES OF PEST MONITORING • Predict and evaluate potential key pest problems and non-target effects • Provides info for choosing and timing appropriate control actions • Evaluates effectiveness of management practices • Establishes a pest history for the specified area
  • 25. BENEFITS OF MONITORING • Greater awareness of pest activity, including changes in pest populations. • Up-to-date information on the health of your plants. • Data that can be used to compare pest outbreaks from season to season. • Early detection of pest problems, resulting in the availability of more management options.
  • 26. SAMPLING TECHNIQUES • Sampling technique is important to ensure a representative portion of the crop has been monitored since pest activity is often patchy. • Sampling parameters(e.g. number of samples per padlock and number of leaves per sample) helps sampling consistency. sampling technique includes:- • Sample size • Sample number • Depend on crop type • Crop age • Padlock size
  • 27. SAMPLING TYPES 1. ABSOLUTE SAMPLING- • To count all the pests occurring in a plot • Pests per spatial area • Direct observation/count of pests: easier with static organisms • Total census of pests within a given area 2. RELATIVE SAMPLING- • To measure pest in terms of some values which can be compared over time and space e.g. light trap catch, pheromone trap • Pests per sampling effort i.e. sweeps with a sweep net • Insects/spores per passive or active trap • Partial census: sampling method is not 100% fool proof • Relative measures can be transformed in to absolute measures • This is often the basis for pest management thresholds
  • 28. SAMPLING METHODS BETA SHEET:- Main tool used to sample row crops for pests and beneficial insects. Beta sheets are particularly effective or sampling caterpillars, bugs, aphids and mites. A standard beat sheet is made from yellow or white taroaulin material with heavy dowel on each end. Beta sheets are generally between 1.3-1.5 m wide by 1.5-2.0 m deep (the larger dimension are preferred for taller crops). the extra width on each side catches insects thrown out sideways when sampling and the sheets depth allow it to be draped over the adjacent plant row. this prevents insect being escape through this row. Other various sampling techniques can be used to quantify pest populations in the field, they are:-
  • 29. • In situ counts- visual observation on number of insects on plant canopy(either entire plot or randomly selected plot) • Knock down- collecting insect from an area by removing from crop and (sudden trap)counting • Suction sampling- it is quick and relatively easy way to sample for mirids. its main drawback are unacceptably low sampling efficiency, a propensity to suck up flowers and bees, noisy operation, high purchase cost of the suction machine. • Netting- use of sweep net for hoppers • Narcotized collection- quick moving insects anaesthetised and counting • Trapping- used to sample mobile insects. left out in the field for a period of time, then the number of insects is counted. • Pan trap: blue pan traps for aphids • Pheromone trap: species specific • Sticky trap: sucking insect • Bait trap: Shoot fly and other flies • Emergence trap: for soil insects • Light traps – moths, mosquitoes, beetles
  • 30. • STAGES OF SAMPLING Usually most injurious stage counted but depends on the type of crop, insects, history of insects, influences of biotic and abiotic factors on pest population and insect nature of a damage. • SAMPLE SIZE Sample size differ with nature of pest and crop but large sample size gives accurate result. Sample size will depend on crop type, age and padlock size, and is often in between the ideal number and location of samples and what is practically possible. Sample size should be enough to provide good field representation or coverage
  • 31. DECISION MAKING • Decision regarding when to start control measure depends on the population or damage assessed from the crop. • The pest population is compared to economic threshold level and economic injury level. • When pest level crosses ETL, control measure has to be taken to prevent pest from ETL.
  • 32. BIOASSAY • A bioassay involves use of a biological organism to test for chemical toxicity. • It involves the use of live animal or plant(in vivo) or tissue or cell(in vitro)to determine the biological activity of the substance, such as a hormone or drugs. • Bioassay are typically conducted to measure the effects of a substance on a living organism, such as a hormone or drug. PROPERTIES OF GOOD BIOASSAY:- • Reproducibility (the “litmus test” of science) • Results easily observed and measured • Relatively low cost • Preferably of short duration (less opportunity for confounding factors); more replication • Linear dose-response
  • 33. PURPOSE OF BIOASSAY • Measurements of the pharmacological activity of new or chemically undefined substances. • Investigation of the function of endogenous mediators. • Determination of the side-effect profile, including the degree of the drug toxicity. • Measurement of the concentration of known substances(alternatives to the use of the whole animals have made this use obsolete). • Assessing the amount of pollutants being released by a particular source, such as wastewater or urban runoff. • Determining the specificity of certain enzymes to certain substrates.