大理石纹小鱼适宜筑巢地预测方法的可靠性及应用

A. Burger, F. Waterhouse, J. Deal, D. Lank, D. Donald
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引用次数: 1

摘要

在沿海森林中确定和绘制合适的筑巢栖息地是恢复和管理大理石纹小嘴(Brachyramphus marmoratus)的关键因素,它在加拿大被列为濒危物种。本文综述了三种主要的生境适宜性评估方法的可靠性及其应用:基于gis的植被资源调查(VRI)算法BC模型;航空照片判读(API),基于森林结构的航空照片直接评估;低空航空调查(LLAS),直升机调查评估森林冠层结构和潜在筑巢平台的存在。总的来说,LLAS提供了最可靠的识别,是三种方法中唯一估计森林冠层中潜在筑巢平台的方法。另外两种方法,即API和BC模型,在确定小海豚筑巢的实际栖息地方面,可靠性要低得多。空间尺度和调查强度对三种方法的生境分类均有影响。一般来说,使用LLAS和API的精细尺度(~3 ha)、高强度分类比使用中等尺度(10或100 ha)和/或低强度分类更容易在已知的筑巢地点发现合适的栖息地。即使进行了小规模的高强度应用,仍有15%和25%的已知巢址被划分为“不适合”的LLAS和API栖息地。在中比例尺上应用的所有三种方法似乎都错过了细比例尺筑巢栖息地(即少量合适的树木出现在其他不合适的栖息地)。因此,可以调整已绘制的适宜生境区域以考虑到这种差异,并讨论了这样做的方法。
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The Reliability and Application of Methods Used to Predict Suitable Nesting Habitat for Marbled Murrelets
Identifying and mapping suitable nesting habitat within coastal forests is a key element in the recovery and management of the Marbled Murrelet (Brachyramphus marmoratus), which is listed as Threatened in Canada. This article reviews the reliability and application of three primary methods used to assess habitat suitability: the BC Model, a GIS-based algorithm using Vegetation Resources Inventory (VRI); air photo interpretation (API), direct assessments from air photos based on forest structure; and low-level aerial surveys (LLAS), helicopter surveys assessing forest canopy structure and the presence of potential nest platforms. In general, LLAS provides the most reliable identification and is the only method of the three that estimates the occurrence of potential nest platforms in the forest canopy. The other two methods, API and the BC Model, are substantially less reliable in identifying habitat actually used by nesting murrelets. Spatial scale and survey intensity affect habitat classification using all three methods. Generally, fine-scale (~3 ha), high-intensity classifications with LLAS and API are more likely to detect suitable habitat at known nest sites than those using medium-scale (10s or 100s ha) and/or low-intensity classifications. Even with fine-scale high-intensity application, 15% and 25% of known nest sites were still classified as “unsuitable” habitat with LLAS and API, respectively. All three methods applied at the medium scale for mapping appeared to miss fine-scale nesting habitat (i.e., small numbers of suitable trees occurring in otherwise unsuitable habitat). Areas of mapped suitable habitat can therefore be adjusted to take this discrepancy into account, and methods to do this are discussed.
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