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): 3,5003,500 deaths.

    • Post-DDT (1969): 33 deaths.

    • This represents a reduction in cases of between 99%99\% and 100%100\%.

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: Low concentration in waterphytoplanktonzooplanktonsmall fishlarge fishtop-order predators (e.g., eagles)\text{Low concentration in water} \rightarrow \text{phytoplankton} \rightarrow \text{zooplankton} \rightarrow \text{small fish} \rightarrow \text{large fish} \rightarrow \text{top-order predators (e.g., eagles)}.

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: 600600 to 800800 breeding pairs.

    • 1940s: DDT production and distribution begin.

    • 1959: DDT usage reaches its peak.

    • 1970s: The breeding population dropped to just 6060 pairs.

    • 1972: The U.S. bans DDT usage.

    • 2001: After significant conservation effort, the population recovered to 646646 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 99%99\% since the early 1980s.

    • Three species of Gyps vultures had a combined population of 40,000,00040,000,000 in the early 1980s.

    • By 2017, the total population of these three species dropped to approximately 19,00019,000.

  • 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 200200 agricultural chemicals, including rodenticides.

  • Toxicological Thresholds:

    • Toxicology levels are measured in milligrams per kilogram (mg/kgmg/kg) of liver.

    • Low Toxicity/Exposure: Up to 0.1mg/kg0.1\,mg/kg.

    • Lethal Range: Values between 0.1mg/kg0.1\,mg/kg and 0.5mg/kg0.5\,mg/kg are the ballpark where owls tend to die.

    • Definite Death: Values above 0.5mg/kg0.5\,mg/kg.

  • Findings by Species:

    • Power Flowers: Approximately 33%33\% of tested animals were in the lethal toxicity range.

    • Tawny Frogmouths: Almost 70%70\% showed exposure; 42%42\% had levels likely to cause death, despite predominantly eating insects.

    • Boobooks: Approximately 17%17\% 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.