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Promoting Resource Efficiency in Small & Medium size ... - UNEP

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What Type of Waste Does<br />

Your Bus<strong>in</strong>ess Produce?<br />

Scrap Metal/Plastic/<br />

Some Paper<br />

Evaluate Waste<br />

Leav<strong>in</strong>g Your Bus<strong>in</strong>ess<br />

General Trash<br />

Industrial Waste<br />

Sewer Waste<br />

e. Assembl<strong>in</strong>g <strong>in</strong>put and output <strong>in</strong>formation for unit<br />

operations<br />

The total of what goes <strong>in</strong>to a process must equal the total of what<br />

comes out. Prepar<strong>in</strong>g a material balance is designed to ga<strong>in</strong> a better<br />

understand<strong>in</strong>g of the <strong>in</strong>puts and outputs, especially waste, of a unit<br />

operation so that areas where <strong>in</strong>formation is <strong>in</strong>accurate or lack<strong>in</strong>g<br />

can be identified.<br />

Recycle<br />

Requires County License<br />

Reduced Regulatory Requirements<br />

Non-Hazardous<br />

Characteristic<br />

Wastes<br />

Ignitable<br />

Corrosive<br />

Reactive<br />

Toxic<br />

Oxidiser<br />

Hazardous<br />

Figure 39: Example of a waste flowchart 63<br />

May Require Futher<br />

Evaluation to Determ<strong>in</strong>e<br />

if Hazardous<br />

Specifically Listed<br />

Wastes From:<br />

Solvents<br />

Electroplat<strong>in</strong>g<br />

Manufacture Process<br />

PCB’s<br />

Acute Hazardous<br />

Toxic Discard<br />

Special Wastes<br />

Fluorescent Tubes<br />

Batteries<br />

Computers<br />

Electronics<br />

Silver Wastes<br />

Oil<br />

Antifreeze<br />

materials and their use, and wastewater treatment and disposal.<br />

Discuss the sequence of activities with the relevant people <strong>in</strong> your<br />

company and confirm that this is correct.<br />

Review the flowchart with your workers and your bus<strong>in</strong>ess partners:<br />

- Workers and supervisors<br />

- Suppliers<br />

- Transporters<br />

- Customers<br />

- Other relevant stakeholders<br />

Check if they agree that the process is drawn accurately.<br />

Step 2: Create a Material Balance<br />

A material balance may be def<strong>in</strong>ed as a precise account of the <strong>in</strong>puts and<br />

outputs of an operation. The general form quoted for a mass balance is<br />

that the mass that enters a system must, by conservation of mass, either<br />

leave the system or accumulate with<strong>in</strong> the system.<br />

Steps:<br />

a. Determ<strong>in</strong>e <strong>in</strong>puts<br />

Quantify <strong>in</strong>puts such as raw materials, chemicals, water, air and<br />

power<br />

b. Measure current levels of waste reuse/recycl<strong>in</strong>g<br />

Take notice of the number of b<strong>in</strong>s or conta<strong>in</strong>ers that are removed.<br />

You might want to weigh them (or some of them and extrapolate).<br />

Some waste can be directly reused and may be transferred from one<br />

unit to another; others require some modification before they are<br />

suitable for reuse <strong>in</strong> a process. Quantify reuse waste streams.<br />

c. Quantify process outputs<br />

Outputs <strong>in</strong>clude primary product, by-products, wastewater, gaseous<br />

wastes, liquid and solid wastes that need to be stored or sent off-site<br />

for disposal and reusable or recyclable wastes.<br />

d. Account<strong>in</strong>g for off-site waste<br />

The process may produce waste that cannot be treated on-site.<br />

These need to be transported off-site for treatment and disposal.<br />

Waste of this type is usually non-aqueous liquids, sludge or solids.<br />

M<strong>in</strong>imisation of these wastes yields a direct cost benefit.<br />

f. Deriv<strong>in</strong>g a prelim<strong>in</strong>ary material balance for unit<br />

operations<br />

Make use of the conservation law: what goes <strong>in</strong> must come out. This<br />

must work out for the plant as a whole, as well as for each of the<br />

<strong>in</strong>dividual units and activities.<br />

g Evaluat<strong>in</strong>g the material balance<br />

The <strong>in</strong>dividual and sum totals mak<strong>in</strong>g up the material balance<br />

should be reviewed to determ<strong>in</strong>e <strong>in</strong>formation gaps and <strong>in</strong>accuracies.<br />

If outputs are less than <strong>in</strong>puts look for potential losses or waste<br />

discharges. Outputs may appear to be greater than <strong>in</strong>puts if large<br />

measurement or estimat<strong>in</strong>g errors are made or some <strong>in</strong>puts have<br />

been overlooked.<br />

h. Ref<strong>in</strong><strong>in</strong>g the material balance<br />

Do the material balance <strong>in</strong> iterations: do not struggle for 100%<br />

accuracy of data from the very beg<strong>in</strong>n<strong>in</strong>g. Make the process a<br />

learn<strong>in</strong>g process, <strong>in</strong> which you and your team gradually build a<br />

better understand<strong>in</strong>g of material flows, waste generation and waste<br />

sources.<br />

Step 3: Locate Sources of Waste<br />

Waste generation might be related to impurities <strong>in</strong> the raw materials,<br />

the production process itself (a chemical reaction might generate a<br />

certa<strong>in</strong> quantity of byproducts; lubrication oils accumulate dirt over<br />

time and need to be replaced), the organisation of the process (startup<br />

waste, shut down waste, expired chemicals), clean<strong>in</strong>g (cast-off<br />

materials cleaned out of mach<strong>in</strong>ery <strong>in</strong> between batches of different<br />

products), to quality control (off-spec products).<br />

Tak<strong>in</strong>g a bird’s-eye-view of the production process will help identify<br />

various sources of waste and take measures to prevent it. Waste<br />

reduction at the source is the first priority. What cannot be avoided<br />

should be reused (for example waste textiles as clean<strong>in</strong>g rags, waste<br />

sheet metal for sett<strong>in</strong>g up mach<strong>in</strong>es) and what cannot be reused<br />

should be recycled (for example metals, but also solvents, fibres).<br />

The follow<strong>in</strong>g are some examples for waste m<strong>in</strong>imisation:<br />

<strong>Resource</strong> optimisation: Optimised use of raw materials can mean<br />

optimis<strong>in</strong>g the pattern <strong>in</strong> which the parts <strong>in</strong> stamp<strong>in</strong>g are laid out on<br />

the sheet metal to m<strong>in</strong>imise the area used.<br />

Reuse of scrap: Scraps can be taken back <strong>in</strong>to the process; paper<br />

mills return damaged paper from breakage <strong>in</strong>to the pulper to recover<br />

the fibres.<br />

Improved quality control and process monitor<strong>in</strong>g: Inspection and<br />

even better automated cont<strong>in</strong>uous monitor<strong>in</strong>g equipment can help to<br />

m<strong>in</strong>imise lost batches, because it helps to identify process problems<br />

early.<br />

Waste exchanges: Waste from one process can become raw material<br />

for another: spent catalysts of a chemical company can become raw<br />

material <strong>in</strong> the production of catalysts, collected motor oil can be<br />

used as fuel <strong>in</strong> a boiler.<br />

63) Wash<strong>in</strong>gton County, Does your bus<strong>in</strong>ess generate hazardous waste? 2008.<br />

69

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