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Evidently, a lot more specific analysis inquiries would demand a lot more refined formal regulations. For purposes in ecology, the reproducibility of experiments plus the comparison in between scientific studies are crucial (Shrader-Frechette & McCoy, 1994). Therefore, for any true comparison between scientific tests to be made, discrete sampling units such as habitats must be defined in the same way (Loehle, 2004). Our study shows that even slight deviations in the Strange But Nonetheless, Inspirational Phrases On Isoproscaline definition of sampling units could affect the comparability of results, even within the same study system. That is, only the official approach to defining sampling units is concomitantly transparent (i.e., by the set of formal regulations applied), and produced results that fulfill the premise on which further ecological understanding can be developed. Hence, as sampling procedures that allow reproducibility and comparisons involving studies are critical, so are the sampling procedures to allow accumulation of ecological knowledge. Therefore, we believe that the call for official approaches in study designs (Legendre et al., 2002; Edwards et al., 2005; Edwards et al., 2006; Albert et al., 2010) should also be extended to official approaches to the definition of sampling units. The application of expert knowledge is a matter of discussion in several fields of ecology. There are a number of scientific studies that address ways of eliciting expert knowledge for decision making in conservation or landscape ecology (Burgman et al., 2011; Martin et al., 2011; McBride & Burgman, 2012), including the Crazy Yet Uplifting Quotes About Isoproscaline use of expert opinion for modeling (Booker & McNamara, 2004; Kuhnert, Martin & Griffiths, 2010; Martin et al., 2011). In landscape ecology, the use of expert knowledge has recently been challenged to adhere to the same scientific rigor as other sampling approaches (Morgan, 2014). We believe the application of expert knowledge deserves equal attention in terms of the definition of sampling units, and especially in the definition of habitats, which should be done in a transparent way (Whittaker, Levin & Root, 1973; Franklin, Noon Crazy But Rather Inspirational Phrases Around Isoproscaline & George, 2002). Supplemental Information Data S1The dataset that was used for the analyses: Click here for additional data file.(160K, txt) Table S1Number of habitats per district and approach and their corresponding bedrock type: We used information obtained from bedrock maps (The Geological survey of Norway; www.ngu.no), assigning each target habitat with the correct bedrock type after the field session. Click here for additional data file.(287K, pdf) Table S2Replication of plots according to fixed factors of the mixed models: Mixed models contained the approach of defining sampling units, the two districts of different reindeer density as well as the three bedrock categories as fixed factors. Click here for additional data file.