Waste management in Antarctica (Part 1)

by Pamela da Costa
03/11/2026

Old fuel drums near Beaver Lake. The lake was discovered in 1956 during an Australian expedition. In September 1957, Australian scientists set up a base camp here, using the lake as a landing strip for aeroplanes. (Photo: AAD / M. Woolridge)

Can waste management practices in Antarctica provide a model of sustainability for extreme environments?

The way societies have managed waste has evolved over time in response to emerging priorities, and Antarctica is no exception.

Waste management in Antarctica has evolved from a logistical necessity to a global standard for environmental protection. Through the Madrid Protocol and other complementary instruments, the Antarctic Treaty System has managed to converge on shared regulations that prioritize the integrity of fragile ecosystems.

In Antarctica, scientific and logistical activities -related to the stations- generate different categories of waste that require environmentally controlled management. These include wastewater and domestic sewage, liquid chemical waste, combustible solid waste, non-combustible solid waste, medical and electronic waste, and gaseous emissions associated mainly with the use of fuels and power generation systems. These categories reflect the diversity of waste streams produced in a remote environment, where proper management is essential to minimize environmental impact.

In addition, we must bear in mind that there, each person is an environmental operator and must respond to reducing the volume of waste. This article analyzes the pillars of this model on Antarctic stations and offers elements of judgment on its consideration.

Foto: OpenAI

A paradigm of environmental governance.

To understand the current challenges of waste management in Antarctica, it is necessary to look back at the history of human activity on the continent. Prior to the 1970s, waste generated in Antarctic operations was commonly abandoned, buried, or openly incinerated, as no specific regulations, environmental remediation principles, or shared standards existed to guide proper management practices.

From the 1970s until the adoption of the Madrid Protocol, waste management practices in Antarctica began to evolve gradually, influenced by the guidelines and codes of conduct promoted by SCAR, as well as recommendations developed within the Antarctic Treaty System. Following the entry into force of this international agreement, the regulatory framework became progressively stronger and more binding, incorporating concrete measures such as the prohibition of open-air waste burning, restrictions on the introduction of hazardous materials and certain single-use plastics, and requirements for waste classification, compaction, and removal from the continent to the country of origin.

The mandatory development of waste management plans with the respective environmental assessments, and cleanup actions on historically contaminated sites are also part of the comprehensive management process.

In this context, waste management in Antarctica is not only an issue of environmental contamination, but also a challenge with potential implications for ecological biosecurity. Organic waste, in particular, may facilitate the aggregation of non-native species and the formation of artificial microhabitats for fungi and bacteria, thereby enabling the unintentional transport of associated organisms that can act as vectors of emerging diseases.

Avian influenza provides a relevant example in this regard. Certain categories of waste, especially organic materials or residues that may attract scavenging birds such as skuas and gulls, known carriers of pathogens, can create ecological points of contact between wildlife, human activity, and waste disposal sites. In this sense, high-quality waste management practices could indirectly reduce interspecies contact and contribute to lowering the risk of pathogen transmission in Antarctic ecosystems.

On the other hand, it should be noted that treatment policies do not always eliminate chemical or pharmaceutical contaminants; we cannot forget non-native species, which often arrive through human activities (cargo, food, clothing, equipment, containers, construction materials). Here, organic waste, cargo and packaging waste, wood, cardboard, textiles, and contaminated sediments can be vectors and hosts.

We must also consider that scientific activity itself is fundamental to the protection of the Antarctic environment; however, at the same time, it depends on tangible processes and elements that generate waste that the system itself must control.

As the first link in the management system, waste reduction must be considered the primary priority.

Waste is stored separately for disposal. (Photo: Pamela da Costa)

Minimizing human impact in Antarctica requires close coordination between international governance and on-the-ground operational management. In this unique environment, the principle of controlling environmental risks before they occur becomes central to decision-making.

International cooperation serves as the driving force behind this system, enabling multiple countries to apply shared and rigorous standards under the framework of the Antarctic Treaty System. It also allows for international inspections, which function as a key mechanism for verifying compliance and reinforcing the broader principle of environmental prevention.

Currently, despite differences in operational scale and technological capacity among countries operating Antarctic stations, they have been able to converge through their respective national programs on a transition from local waste disposal practices to a management model based on removal from the continent, including limited on-site wastewater treatment and controlled incineration. This responds to the principle of minimal environmental intervention in situ rather than technological self-sufficiency.

So, is the principle of minimal environmental intervention a necessary ecological safeguard, or a normative barrier that constrains the experimentation of advanced circular economy models in polar contexts?

Take this question with you. Reflect on it. Challenge it. See you here next week!

Appendix: Bibliographical References

  1. Antarctic Treaty Secretariat (1991).  Protocol to the Antarctic Treaty on Environmental Protection (Madrid Protocol). Annex II: Antarctic Flora and Fauna; Annex III: Waste Disposal and Management.
  2. Antarctic Treaty Secretariat  (2005). Annex VI to the Madrid Protocol: Liability arising from environmental emergencies.
  3. COMNAP (2006) (Council of Managers of National Antarctic Programs). Waste Management Monitoring Guidelines for the Antarctic.
  4. Chamber of Waste Management Companies of Uruguay (Feb. 2026) Technical inquiries.  Inicio – CEGRU
  5. Corbo, Richard (2019) Review of the regulatory framework and guidelines for the development of environmental management plans for Antarctic bases: Inputs for the development of an environmental management plan for the Artigas Antarctic Scientific Base. CURE,University of the Republic.
  6. Gröndahl, F., et al. (2009). “Challenges for the Environmental Management of Antarctic Research Stations”. Polar Research.
  7. Antarctic Treaty Secretariat,Resolución 1 (2019). Antarctic Clean-Up Manual
  8. Declaration of generative AI

Author: Pamela da Costa

Since 2017, I have been working at the Uruguayan Antarctic Institute. In this context, I have participated in official missions with RCTA-CPA, RAPAL, and Antarctica. I have academic training in International Relations, complemented by specialized studies in scientific diplomacy, polar studies, climate change, foreign policy, and international security, along with an internship at the Antarctic Treaty Secretariat in 2024, which has allowed me to develop specific technical knowledge about the functioning of the System, its negotiation processes, and its international cooperation dynamics.Deeply engaged with Antarctic issues, I seek to use this topic as a springboard for innovation, promoting actions that generate new research questions.