Lecture 15 - Silent Killers: Toxins, Chemicals, and Wildlife Conservation
Introduction: The Human Population and the Chemical Management Revolution
The Rise of the Human Population and Resource Demand:
The human population has experienced enormous growth, correlating with a significantly increased need for resources.
This growth was facilitated by developments that allowed humans to battle diseases and intensify agricultural practices.
Solutions were required to manage species that compromised human lifestyles, including those affecting agricultural productivity (rodents, insects) and those acting as disease vectors (mosquitoes carrying malaria).
The Chemical Management Revolution:
Human affluence and the current population size are linked to the ability to synthesize and manage chemicals.
The 1940s marked the rise of the first synthetic chemicals designed to protect and intensify agriculture.
These chemicals were vital for increasing productivity and decreasing outbreaks of diseases significant to human development.
Emerging Risks:
Despite the benefits to human development, risks associated with these chemicals began to emerge regarding both human health and wildlife health.
Rachel Carson and the Silent Spring
The Warning:
American marine biologist Rachel Carson was one of the first to raise concerns about synthetic chemicals.
Her primary concern was DDT, one of the earliest synthetic insecticides, which was initially regarded as a "wonder chemical."
DDT Applications:
DDT was used to nearly eradicate malaria in certain regions.
It was sprayed over agricultural crops, effectively wiping out insect pests.
It was persistent, meaning it did not require frequent re-application.
Silent Spring (1962):
Carson published this book in 1962 to highlight the massive human and ecosystem health issues associated with DDT usage.
Consequently, DDT was banned throughout much of the world by the 1980s, though it retains limited usage in specific areas.
Empirical Success of DDT in Malaria Control:
Pre- and post-usage data for mosquito control in Cuba illustrates the effectiveness of the drug:
Pre-DDT (1962): deaths.
Post-DDT (1969): deaths.
This represents a reduction in cases of between and .
Toxicology and Bioaccumulation of DDT
Chemical Stability:
DDT is extremely stable and does not break down quickly through biological activity or water exposure.
It persists in the environment for 20 to 30+ years.
Bioaccumulation and Biomagnification:
Bioaccumulation: Because DDT does not break down, it is deposited in the fatty tissues of animals and is not easily excreted.
Biomagnification: Predators receive a concentrated dose when they consume prey containing DDT, meaning the chemical is magnified as it moves higher up the food chain.
Aquatic Food Chain Transmission:
DDT is not soluble in water. It moves through river systems and accumulates in lakes.
The process follows this path: .
The Case of the Bald Eagle in the United States
Population Impact:
The Bald Eagle, a national symbol of the United States, suffered high concentrations of DDT because it is a fish-eating predator.
The chemical caused widespread breeding failure across the Continental United States and parts of Northern America into Canada.
Mechanism of Failure: Eggshell Thinning:
DDT impacted the birds' capacity to produce healthy eggs.
The shells thinned to a point where they could not support the weight of the adult bird during incubation, leading to broken eggs.
Population Trends in Chesapeake Bay:
1930s: to breeding pairs.
1940s: DDT production and distribution begin.
1959: DDT usage reaches its peak.
1970s: The breeding population dropped to just pairs.
1972: The U.S. bans DDT usage.
2001: After significant conservation effort, the population recovered to breeding pairs.
2020: The population has experienced a "boom" due to modern protection and the removal of DDT impacts.
Persistence in Australia:
Tests on Power Flowers (likely reference to Powerful Owls) in 2021/2022 still detected DDE (a breakdown product of DDT).
This occurred roughly 40 years after the chemical was banned in Australia in the early 1980s.
The Asian Vulture Crisis
Dramatic Population Crashes:
Across India and South Asia, vulture populations have declined by as much as since the early 1980s.
Three species of Gyps vultures had a combined population of in the early 1980s.
By 2017, the total population of these three species dropped to approximately .
Detection of the Decline:
The decline was noted in the mid-1990s by naturalists and the Parsi religious group, who utilize vultures to consume bodies in "Towers of Silence."
Farmers также noticed vultures were no longer clearing dead cattle.
The Culprit: Diclofenac:
In 2003, research identified Diclofenac, an anti-inflammatory drug used for humans and livestock (cattle).
Because cattle are often sacred in India, they are left in fields after death, where vultures consume them.
Vultures are highly intolerant to Diclofenac; very small doses cause kidney failure and rapid death.
Ecological and Health Consequences:
Vultures are a keystone species responsible for cleaning up carrion and recycling the system.
Their unique digestive systems kill diseases that might otherwise spread.
Without vultures, carcasses rot, leading to viruses and bacteria infecting water sources.
Mammalian Scavengers: Dog populations increased to eat the cattle, but they lack the vulture's gut capacity to neutralize disease.
This has led to the emergence of health issues such as rabies carried by large feral dog populations.
Regulatory Management:
Diclofenac was banned for veterinary use in India in 2006, though enforcement is difficult.
Anticoagulant Rodenticides
History and Context:
Management of rodents is a massive social issue related to food security. Outbreaks historically led to human starvation.
Techniques involve an "arms race" where humans develop poisons and rats evolve resistance.
Mechanism of Action:
Anticoagulant rodenticides block the Vitamin K cycle, which is essential for blood clotting.
Animals suffer internal or external hemorrhaging from slight injuries, eventually bleeding out.
Generations of Rodenticides:
First Generation (1950s):
Based on Warfarin (a human blood thinner).
Required high doses and multiple feedings (e.g., twice a week) because the body could excrete it fairly readily.
Widespread genetic resistance eventually developed.
Second Generation (SGARs):
Very powerful; require only a single feed to be lethal.
Slow-acting (takes about a week for the animal to die), allowing the poisoned rodent to continue feeding and remain exposed to predators.
Terminology of Poisoning:
Non-target species: Species that consume the poison directly but were not the intended target.
Secondary poisoning: Predators (like owls) eat a rodent that has already consumed the poison, allowing it to move through the food chain.
Rodenticide Impact on Australian Wildlife
The Study:
Research conducted around 2020-2021 during lockdowns investigated deaths in Power Flowers, Tawny Frogmouths, Boobooks, and Barn Owls.
Livers were tested for heavy metals and over agricultural chemicals, including rodenticides.
Toxicological Thresholds:
Toxicology levels are measured in milligrams per kilogram () of liver.
Low Toxicity/Exposure: Up to .
Lethal Range: Values between and are the ballpark where owls tend to die.
Definite Death: Values above .
Findings by Species:
Power Flowers: Approximately of tested animals were in the lethal toxicity range.
Tawny Frogmouths: Almost showed exposure; had levels likely to cause death, despite predominantly eating insects.
Boobooks: Approximately were in the definitely lethal category.
Barn Owls: Showed heavy impacts similar to global trends.
Chemical Types Detected:
Brodifacoum: The most common active ingredient (found in hardware stores like Bunnings).
Other actives include Bromadiolone and Flocoumafen.
Many animals showed exposure to multiple types of rodenticides simultaneously, suggesting repeated exposure events.