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Upon EDTA treatment thylakoids lose the chloroplast coupling factor 1 (CF1) part of their ATP synthase, CF0CF1, this exposes the proton channel, CF0. The previously established ability of the CF1 subunit delta to block the proton leak through CF0 prompted us to study (a) the ability of complete CF1 and, for comparison, CF1 lacking the delta subunit to block proton leakage and thereby to reconstitute structurally some photophosphorylation activity of the remaining CF0CF1 molecules and (b) their ability to form functional enzymes (functional reconstitution). In order to discriminate between activities caused by added CF1 or CF1(-delta) and remaining CF0CF1, the former were inhibited by chemical modification of subunit beta by N,N'-dicyclohexyl carbodiimide (DCCD) and the latter by tentoxin. We found that added CF1 acted both structurally and functionally while added DCCD-treated CF1 (DCCD-CF1) acted only structurally. In contrast to previous observations, CF1(-delta) and DCCD-CF1(-delta) also acted structurally although the reduction of proton leakage was smaller than with DCCD-CF1. Hence there was no functional reconstitution without subunit delta present. Previous studies indicated that only a small fraction of exposed CF0 is highly conducting and that this small fraction is distinguished by its high affinity for added CF1. The results of this study point rather to a wider distribution of CF0 conductance states and binding affinities. 相似文献
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Jonathan M. Conard Jeremy A. Baumgardt Philip S. Gipson Donald P. Althoff 《Acta theriologica》2008,53(2):143-156
Assessing species richness of small mammal communities is an important research objective for many live-trapping studies designed
to assess or monitor biological diversity. We tested the effectiveness and efficiency of various trap densities for determining
estimates and counts of small mammal species richness. Trapping was conducted in grassland habitats in northeastern Kansas
during spring and fall of 2002 and 2003. Estimates and counts of species richness were higher at increased trap densities.
This effect appeared to be primarily due to the higher number of individuals sampled at higher trap densities. At least 3
nights duration was needed to produce a stable estimate of species richness for the range of trap densities tested (9–144
trap stations/ha). Higher trap densities generally reached stable richness estimates in fewer nights than low density trapping
arrangements. Given that counts and estimates of species richness were influenced by trap density and sampling duration, it
is critical that these parameters are selected to most effectively meet research objectives. 相似文献