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page 74 of 142 <strong>RIVM</strong> <strong>report</strong> 773301 001 / NRP <strong>report</strong> 410200 051<br />

For k we use as GHIDXOWVN DQG, depending on the regions. In practice the value can<br />

vary between 0.005-0.4 year. N = 0.95 when using k = 0.21; doubling or halving the k-value gives the<br />

range for N of 0.90-0.98 (the extremes mentioned give 0.82-1.00 as range).<br />

To calculate the actual emissions in year W the methane generated should be corrected for any<br />

amount recovered 5 (e.g. used energetically or flared) and the fraction of methane 2; that is oxidised<br />

in the upper layers of waste and in the site cover material, before it is released to the atmosphere:<br />

where:<br />

R(t) = Recovered amount of CH 4 [Gg/yr]; GHIDXOW<br />

OX = Oxidation factor [fraction]; H[FHSW IRU2(&'DQG(,7 (IPCC default is 0)<br />

Results of this model are presented in Fig. 4.6.<br />

Emissions E(t) = [G(t) - R(t)] * (1 - OX)<br />

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According to our analysis, global total net landfill emissions increased from 15 to 23 Gg in the 1970-<br />

1995 period. This includes the effect of increasing amounts of methane being recovered and<br />

combustion for energy purposes or flared, which increased from virtually 0 to 2.5 and 4.3 Gg in 1990<br />

and 1995, respectively (see Table 4.9). Figure 4.6 clearly shows the impact on emissions from the<br />

USA in the early '90s. Table 4.12 shows how the amount of waste deposited into landfills has<br />

increased over time but started to decrease in the 1990's in the USA and in the countries of the former<br />

USSR.

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