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Eleven 22007 1735 fifty one 850 5350 zero. 21 2. 39 five. 60 2. fifty two zero. 23 eleven. 50 27 four. eleven 22007 2949 fifty one 1445 5350 real distance zero. 21 2. 39 20. 00 nine. 00 zero. 23 eleven. 50 27 four. eleven 22007 2949 fifty one 1445 5350 elevated distance Domesticated ﬂoodplain elevated distance Wild real distance anticipated Values for Variables integrated within the Simulation 1. 18 thirteen. fifty three zero. 25 zero. eleven zero. 23 eleven. 50 27 four. eleven 22007 867 fifty one 425 5350 real distance Wild (continued) zero. 88 10. 17 zero. 25 zero. eleven zero. 23 eleven. 50 27 four. eleven 22007 1154 fifty one 565 5350 real distance Domesticated hillside 275 5780 zero zero. 00 zero. 00 thirteen. 29 elevated distance 1937 1686 a hundred zero. 14 zero. 30 five. ninety four genuine distance 589 5874 a hundred zero. 14 zero. 30 12. forty two elevated distance Domesticated ﬂoodplain chenopod 1077 1618 zero zero. 00 zero. 00 eight. sixty nine genuine distance Wild 1872 208 a hundred zero. 10 zero. sixty one 6. ninety six real distance Domesticated hillside 2196 seventy two zero zero. 00 zero. 00 nine. 28 real distance 1029 5780 zero zero. 00 zero. 00 15. seventy six elevated distance Wild 3831 1713 a hundred zero. 03 zero. sixty seven five. fifty eight genuine distance 1370 5874 a hundred zero. 05 zero. sixty seven 12. 06 elevated distance Domesticated ﬂoodplain sumpweed 1608 seventy two zero zero. 00 zero. 00 thirteen. sixty four real distance Wild 1923 314 a hundred zero. 07 zero. seventy seven eleven. 05 genuine distance Domesticated hillside c b Asch and Asch 1978; Smith 1987a, 1992; USDA 2002. AOTA 2002. Barlow 2002; Smith 1987a, 1992; Winterhalder and Goland 1997. d Ainslie 2002. observe: All info for the Courthouse Rock case (5. 6 km round-trip distance) are integrated. additionally, values for the 20 km round-trip hypothetical case are given to demonstrate the results of elevated shuttle distance on comparable variables and total go back premiums. See textual content for extra info resources. a go back price kcal/hr 1148 1618 power costsd kcal expended (per load) go back premiums zero zero. 00 zero. 00 6. eighty one guidance time soil guidance, hr/ha/year soil coaching, hr/kg soil practise, hr/load overall time expenditures consistent with load real distance Wild desk three. 1 (continued) expected Values for Variables incorporated within the Simulation from the database of the collage of Vermont division of food and nutrients Sciences. strength expenditure via a 100-lb (45. four kg) individual whereas clearing land and hauling branches, cutting wooden, and digging, spading, and filling a backyard averages 242 kcal/hr. those expenditures replicate use of recent steel instruments; real power charges utilizing stone or wood instruments have been most likely a little better. assortment charges The time spent harvesting chenopod seeds relies either at the approach to assortment and patch features equivalent to the density and spatial distribution of vegetation. The simulation assumes that either Chenopodium and Iva have been harvested by way of hand-stripping. there's a few archaeological proof for uprooting of complete vegetation and garage of Iva as “sheaves” (Jones 1936). In upland events, chenopod crops are inclined to ensue as small clusters inside of greater stands ruled through the similar C. missouriense (Smith 1987a). even supposing upland stands can be fairly dense, they're small and broadly separated. Floodplain stands can also be commonly scattered, even supposing density is very variable.