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Detecting change in advance tree regeneration using forest inventory data: the implications of type II error

机译:使用森林清单数据提前检测树木更新的变化:II型错误的含义

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Achieving adequate and desirable forest regeneration is necessary for maintaining native tree species and forest composition. Advance tree seedling and sapling regeneration is the basis of the next stand and serves as an indicator of future composition. The Pennsylvania Regeneration Study was implemented statewide to monitor regeneration on a subset of Forest Inventory and Analysis plots measured by the U.S. Forest Service. As management techniques are implemented to improve advance regeneration, assessments of the change in the forest resource are needed. When the primary focus is on detecting change, hypothesis tests should have small type Ⅱ (β) error rates. However, most analyses are based on minimizing type I (α) error rates and type Ⅱ error rates can be quite large. When type Ⅱ error rates are high, actual improvements in regeneration can remain undetected and the methods that brought these improvements may be deemed ineffective. The difficulty in detecting significant change in advance regeneration when small type I error rates are given priority is illustrated. For statewide assessments, power (1-β) to detect changes in proportion of area having adequate advance regeneration is relatively weak (≤0.5) when the change is smaller than 0.05. For evaluations conducted at smaller spatial scales, such as wildlife management units, the reduced sample size results in only marginal power even when relatively large changes (>0.20) in area proportion occur. For fixed sample sizes, analysts can consider accepting larger type I error rates to increase the probability of detecting change (smaller type Ⅱ error rates) when it occurs, such that management methods that positively affect regeneration can be identified.
机译:为了保持本地树种和森林组成,有必要实现充分而理想的森林更新。提前进行树木育苗和树苗再生是下一站的基础,并作为未来组成的指标。宾夕法尼亚州再生研究在全州范围内实施,以监控美国森林服务局测量的一部分森林清单和分析地块的再生。随着实施管理技术来改善提前再生,需要评估森林资源的变化。当主要关注于检测变化时,假设检验应具有较小的Ⅱ(β)型错误率。但是,大多数分析都是基于最小化I型(α)错误率,而II型错误率可能会很大。当Ⅱ型错误率很高时,再生的实际改进可能仍未发现,带来这些改进的方法可能被认为是无效的。图示了当优先考虑小I型错误率时检测提前再生中的重大变化的困难。对于全州评估,当变化小于0.05时,检测具有足够提前再生的区域比例变化的能力(1-β)相对较弱(≤0.5)。对于在较小的空间尺度(例如野生动植物管理单位)上进行的评估,减少的样本量只会导致边际功效,即使面积比例发生较大变化(> 0.20)也是如此。对于固定样本量,分析人员可以考虑接受较大的I类错误率,以增加发生变化时发现变化的可能性(较小的Ⅱ类错误率),从而可以确定对再生有积极影响的管理方法。

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