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ESA Document - Emits - ESA

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s<br />

HMM<br />

Assessment Study<br />

Report: CDF-20(A)<br />

February 2004<br />

page 160 of 422<br />

A greenhouse has not been introduced at this stage of the study. The study team is aware of the<br />

positive impact of the greenhouse on the different functions of a LSS, the nutrition of the crew<br />

and on the crew psychology. On the basis of preliminary knowledge, a greenhouse would<br />

provide::<br />

• A high degree of closure of carbon dioxide to oxygen conversion<br />

• A high degree of water loop closure<br />

• A high percentage of fresh food to the crew<br />

However, it would cause an increase in structural mass and power requirements that perhaps<br />

offset the gain of mass on the LSS. Therefore, at this stage of the study and the incomplete tradeoff<br />

between LSS with greenhouse and LSS without greenhouse, the greenhouse was not<br />

considered.<br />

3.3.2.3 Waste management strategy<br />

The long duration of this mission inherently involves the production of substantial amounts of<br />

both organic and inorganic solid waste. This amount adds up to several tonness and has to be<br />

taken into account and dealt with in an efficient way. Several options were considered for waste<br />

management. It was decided to jettison the generated solid waste using existing airlocks to<br />

minimise the mass penalties of the mission. However, some treatment and storage is still<br />

necessary before jettisoning. This treatment depends on the nature of the waste and can be<br />

described as follows.<br />

Waste treatment strategy<br />

The handling of the inorganic waste (i.e. cleaning supplies, hygiene supplies, waste collection<br />

supplies, etc) is somewhat easier than for organic waste as it does not require because much<br />

treatment. Care must be taken in correctly classifying the nature of the waste. Supplies classified<br />

as inorganic upon launch become organic waste upon use by the crew.<br />

The first step in the management of the inorganic waste would be to compact it to reduce its<br />

volume. Mass reduction is possible by reducing the waste reusable solid, gaseous and liquid<br />

compounds. After compaction, decontamination and bioresistant storage would be sufficient to<br />

have the inorganic waste safely stored before jettisoning.<br />

The management of the organic waste (i.e. used tissues, faecal material, hair and skin material,<br />

nail clippings, food leftovers, etc) is more complicated and it requires waste stabilization. Three<br />

main technologies could be used for this purpose: chemical stabilization, sterilization or<br />

lyophilization (commonly referred to as freeze drying). Mass and power considerations, and<br />

assessing their technology readiness level, lyophilization looks most promising for the reduction<br />

of the organic waste.<br />

Lyophilization is the process of removing water from a product by sublimation and desorption. It<br />

is performed in lyophilization equipment which consists of a drying chamber with temperature<br />

controlled shelves, a condenser to trap water removed from the product, a cooling system to<br />

supply refrigerant to the shelves and condenser, and a vacuum system to reduce the pressure in<br />

the chamber and condenser to facilitate the drying process. Lyophilizers come in a wide variety<br />

of sizes and configurations and can be equipped with options that allow system controls to range<br />

from fully manual to completely automated. Lyophilization cycles consist of three phases:

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