Review by Peer 307 on manuscript: Manuscript title censored. Revision recommendation: Withdraw

Similar documents
Goal of the Lecture. Lecture Structure. FWF 410: Wildlife Habitat Evaluation. To introduce students to the basic steps of wildlife habitat evaluation.

Woodpecker Habitat After the Fire

3.15 SNAG AND SNAG ASSOCIATED SPECIES

Title: Plumas-Lassen Area Study Module on Landbird Abundance, Distribution, and Habitat Relationships in Burned Areas.

Northern deciduous forest as wildlife habitat. Tom Paragi Alaska Department of Fish and Game Fairbanks

Quantification of Lewis s Woodpecker habitat using Forest Inventory and Analysis data

Influence of Beaver Activity, Vegetation Structure, and Surface Water on Riparian Bird Communities along the Upper San Pedro River, Arizona

APPENDIX K HABITAT NEEDS: THE PILEATED WOODPECKER AND OTHER PRIMARY CAVITY EXCAVATORS

Title: Assessing the demographic response of an early seral songbird to intensive forest management

Vancouver Island Land Use Plan Higher Level Plan Order

Vancouver Island Land Use Plan Higher Level Plan Order

Provincial Wildlife Tree Policy and Management Recommendations

Bird Response to Forest Management. Chris Moorman, PhD Fisheries, Wildlife, and Conservation Biology NCSU

Silvicultural Effectiveness Monitoring Manual for Ontario

Wildlife Habitat as it relates to Forestry

Habitat Quality Models, Species at Risk, and Wildlife VECs Presentation for the Clean Environment Commission Keeyask Generation Station Hearings

College of Food and Agricultural Sciences Department of Plant Production PhD in Range Sciences and Forestry. (Courses and Thesis Option)

Overland Park, KS Stream Riparian Corridor Quality Evaluation

Fisheries and Oceans Canada Species at Risk Act. Directive on the Identification of Critical Habitat for Aquatic Species at Risk

What causes trees to die? Lightening strike, disease, insect attack, lack of light, poor growing conditions

in the Americas and we tested whether this overlap is (a) higher than if the species had migrated

MURPHY DRAIN CATCHMENT

The Science Behind Forest Riparian Protection in the Pacific Northwest States By George Ice, Summer 2004

NEOTROPICAL MIGRATORY BIRDS

Wildlife Management Planning Guidelines for the South Texas Plains Ecoregion

Application of Uneven- aged Management. What is Uneven-age??? Age Classes. Important Terminology, Concepts & Methodology. defining

THREE-TOED WOODPECKER YEAR-ROUND HABITAT

National Wildlife Federation s Eco-Schools USA-Learning About Forests Post-Action Audit, Grades 3-5

The Influence of Microhabitat on Nest Tree Selection of Southern Flying Squirrels

5/23/2013 Draft dbh between trees with and without nest cavities was not influenced by thinning treatment (Table 4) nor tree kill treatment.

inappropriate to define the growing season length (GLS) based on NEE.

Ecology A Study of Relationships

Appendix C. Consistency With Eastside Screens. Salvage Recovery Project

This Notice applies to the Squamish Forest District. Schedule 1. 1) Marbled Murrelet (Brachyramphus marmoratus) Amount:

Table 4.21 Univariate statistics of patch edge-to-area ratios in the FMA area Edge-To-Area (m/m 2 )

Central Bedfordshire - Natural Capital in Planning

THE JACKSON CREEK OLD-GROWTH FOREST: A SIGNIFICANT WOODLAND IN PETERBOROUGH, ONTARIO Preliminary Results Bulletin #1, March 2016

Characteristics of Snags Used by the Pileated Woodpecker (Dryocopus pileatus) in Old-Growth Red and Eastern White Pine Forests of Temagami, Ontario

Restoring Old-Growth Characteristics

Kelly Burnett 1 Gordon Reeves 1 Dan Miller 2. Sharon Clarke 3 Kelly Christiansen 1 Ken Vance-Borland 3

Wildlife Management Intensity Standards

2017 Regional Envirothon

24. Wildlife Habitat on Farmland

ENR 5340 Syllabus Page 1

Sampling vegetation is important for managing wildlife. Vegetation provides species

California Spotted Owl: Current Trends and Future Management

Avian Habitat Considerations in Northern Hardwoods Silviculture

Appendix J-1 Marking Guidelines Alternative 4 GTR 220

Patch Area and Connectivity Promote Biodiversity for Birds in Urban Landscapes

Updated Scoping Information. Proposed Vallenar Young-growth Project

Forest Edge Effects Study

Status and Trends in Forest Habitat Types of the Boreal Hardwood Transition

Pacific Northwest Old-Growth Forest Concept Mapping

[ CUTTING FOR WILDLIFE ] FOREST HARVEST AND THE GREAT GRAY OWL

3. The poor condition of Connecticut s forests in the late 1800s and early 1900s helped spur the conservation movement in CT.

Scientific Literature Review of Forest Management Effects on Riparian Functions for Anadromous Salmonids

Schoolyard Biodiversity

Management Indicator Species (MIS) Report - Part II

REFORESTATION AFTER HARVEST

The role of forest disturbance in habitat relationships and population ecology of Spruce Grouse.

Managing Forests For Wildlife 3/13/2017 1

Effects of Future Forest Harvest on Wildlife Habitat in southeast British Columbia

Characterization of montane ecosystems, their microclimates, and wildlife distribution and abundance across the hydrographic Great Basin

Variable Method Source

Indicators: Characteristics, Qualities and Options. Peter Tango STAR Coordinator

Data and Information Collection for Sustainable Forest Management in Japan

Riparian Forest Ecology & Management. Derek Churchill, Nov 8, 2014

Peter H. Singleton John F. Lehmkuhl. USDA Forest Service Pacific Northwest Research Station Wenatchee Forestry Sciences Lab

STANDARD TERMS FOR DESCRIBING WOOD

The Safe Harbor Program for Red-cockaded Woodpeckers in North Carolina

Appendix Y. ELC and Wildlife Species Habitat Analysis

DRAFT Forested Wetlands in the Mississippi Alluvial Valley (MAV)

Ground Rules Addendum Mountain Pine Beetle Operations

Category V: Undersized trees 78,070 48,015 49,727. Density Classes (stems/ha)

Bechstein s Bat. An introduction for woodland owners 2nd edition Bat Conservation Trust

RE: Comments on Climate Action Reserve White Papers regarding Soil Carbon, Lying Dead Wood, Even-Age Management, and Forest Certification Systems

Developing Pruning Prescriptions. Lesson 5. Objectives: Equipment Needs: Method: 40 minutes

Andrew J. Plantinga Bren School of Environmental Science and Management University of California, Santa Barbara

Managing Forested Wildlife Habitats

PPBio Australasia Metadata HOLLOW BEARING TREES

Data Report: Vegetation Survey at Avian Point Count Stations along Pine Flat Road, in northern Sonoma County, California

National forest inventory and

Effects of artificial watering points on rangeland bird communities

Introduction Appalachian Mts.

EUROPEAN COMMISSION DIRECTORATE-GENERAL FOR AGRICULTURE AND RURAL DEVELOPMENT

ENR 5340 Syllabus Page 1

Analysis of Environmental Data Problem Set Conceptual Foundations: En viro n m e n tal Data Answers

USE OF NON-RIPARIAN HABITATS BY LEAST BELL'S VIREOS 1

A Framework for Monitoring & Evaluating Wildlife Resource Values

PRINCIPLES OF SILVICULTURE FWF 312 SOME SELECTED SILVICULTURAL DEFINITIONS

There are significant errors in the SEPA checklist that need to be remedied.

Making a Plan for Your Woods

WORLD TRADE ORGANIZATION

An assessment of land use change in the Niagara region between 1966 and 1976: An analysis of forest ecosystem services

Appendix J. Forest Plan Amendments. Salvage Recovery Project

UNEVEN-AGED MANAGEMENT NORTHWEST CERTIFIED FORESTRY

Barriers to Recruitment of Cottonwoods on the Northern Range of Yellowstone National Park

01/12/2008. Forest owners. Bio-georaphical Regions in Europe. Green Forest and Management plan a tool for both wood production and nature conservation

Transcription:

Review by Peer 307 on manuscript: Manuscript title censored Revision recommendation: Withdraw ADDED INFO ABOUT PUBLICLY FEATURED REVIEW Author of this peer review is Barbara Frei, PhD candidate at McGill University, Canada PEQ = 4.9 / 5 Peer reviewed by 4 Peers. Introduction The reviewed manuscript (Anonymous authors 2013) describes a study reporting nest-site use on. The authors examined the, hypothesizing that favor. This study also provided various descriptive statistics on nest tree species used in comparisons with tree species in the forests stands, previously existing, nest tree width in comparison to the average of nest patch trees, and lastly distances from nest trees to various 'landmarks'. Merits score: 5.0 / 5. Although the study species is a very well researched in certain parts of its range, the manuscript focuses on an understudied geographic area. Therefore the basic natural history of presented has important merit for the understanding and possible future conservation of this species in the area. Critique score: 5.0 / 5. This manuscript has a number of general and specific problems, ranging from basic grammar and readability, experimental design, statistical analysis, and flaws in the reporting of the findings. I do believe there is valuable data to be published from this research, but as it stands the manuscript is weak and unrefined. This is why I suggest a 'Withdraw' for the manuscript, as I believe the changes that need to be made to this manuscript are many and would be very difficult for the authors to achieve in the time frame allowed. I hope that the following critiques will aid the authors in the refining of the manuscript to allow for re-submission in the future. 1

A general problem of this manuscript includes improper use of terminology and over speculation of habitat selection, given the methods used and data achieved. First, the term 'selection' and 'selective' are used throughout the manuscript. 'Habitat use' and 'habitat selection' have in the past been used interchangeably in the literature and are assumed by some to be the same. This is false. A may 'use' a habitat when it has been shown to forage, roost, nest, and/or show territoriality within it. For example, the in this study demonstrated habitat use at the nest tree scale by. There is no evidence that the used the nest patch or study area. At these scales the proper term would be habitat occupancy. Habitat selection suggests the understanding of complex behavioral and environmental process in which the use of the habitat is the end product of a complex selection process (Jones 2001). True habitat selection studies would be experimental where individuals are given two or more 'choices'. Another general problem involves the experimental design of the research. If nests were found by following sounds of nestlings begging, this means that any nests that (a) failed prior to hatch, (b) were still in egg stage, and (c) had nestlings < 1 week old, would not have been found in the relatively short search window (max. 10 days). This severely biases the results and means only a subset of nests were included in the research. A third general problem lies with the spatial scales and comparisons performed. The authors state that the study is 'spatially comprehensive' but data was collect at the nest tree and nest plot. These are both micro-scale measurements compared to meso-scale (territory) and macro-scale (landscape or range). To compare occupancy one would need to compare occupied vs. unoccupied sites. The authors do so by comparing nest trees to the average of all trees in the nest plot (Line 177-181). It would be far better to compare the nest tree to a randomly selected tree (give certain size limitations) without the nest plot, not an average. In addition, from my understanding on Line 283, the comparisons of nest plot to study plot was an average of the dbh of all trees in a nest plot and then averaged again across nest plots? Generally taking the average of an average is not a good idea. It would be far better to compare occupied nest plots to unoccupied plots within the same study area (see Gutzwiller and Anderson 1987, Li and Martin 1991, Misenhelter and Rotenberry 2000, Newlon and Saab 2011) A fourth general problem is that most statistics performed are descriptive or repeated univariate tests. Typically habitat use or occupancy research uses multivariate statistics, which are superior and far more informative (see Sedgwick and Knopf 1990, Saab et al. 2009, Crampton and Sedinger 2011). A fifth general problem is that basis of the paper, the comparison to. The information presented (i.e. the higher proportion of ) is helpful but not unique compared to other studies, nor is it quantitative support. Few species in fresh wood exclusively. 2

A sixth general problem is that the discussion is weak and mostly comprised of a literature review of existing papers. By rethinking the experimental design and statistic analysis, I believe the authors would find more interesting findings to share and would rely less on the repetition of existing literature to fill the discussion section. The last general problem is the readability and grammar of the manuscript. I completely understand the difficulties in writing in another language and applaud the authors for their grasp of the English language. Still, several sentences are confusing in structure or word use thus I would suggest judicious review by an expert in the English written language. Discussion score: 4.8 / 5. The research on which this manuscript is based has intrinsically importance and once the experimental design and analysis are updated, some interesting findings may be gleaned from the data. Given the under-researched geographic area in which this work is based from, these findings will then undoubtedly have management and conservation merit. References Anonymous authors (2013) (unpublished manuscript) - Peerage of Science Crampton, L.H. & Sedinger, J.S. (2011) Nest-habitat selection by the Phainopepla: congruence across spatial scales but not habitat types. Condor 113: 209-222. Gutzwiller K.J. & Anderson S.H. (1987) Multiscale associations between cavity-nesting birds and features of Wyoming streamside woodlands. Condor 89:534-548. Jackson, J. & Jackson, B. (2004) Ecological relationships between fungi and woodpecker cavity sites. Condor 106: 37-49. Jones, J. (2001) Habitat selection studies in avian ecology: a critical review. Auk 118: 557-562. Li, P. & Martin,T.E. (1991) Nest-site selection and nesting success of cavity-nesting birds in high elevation forest drainages. Auk 108:405-418. Misenhelter, M. & Rotenberry, J.T. (2000) Choices and consequences of habitat occupancy and nest site selection in Sage Sparrows. Ecology 81: 2892-2901. Newlon, K.R. & Saab,V.A. (2011) Nest-site selection and nest survival of Lewis's Woodpecker in aspen riparian woodlands. Condor 113: 183-193. Saab, V., Russell, R.E. & Dudley, J.G. (2009) Nest-site selection by cavity-nesting birds in relation to postfire salvage logging. Forest Ecology and Management 257: 151-159. 3

Sedgwick, J.A. & Knopf, F.L. (1990) Habitat relationships and nest site characteristics of cavitynesting birds in cottonwood floodplains. Journal of Wildlife Management 54: 112-124. Additional comments for authors - line 55-60 a rather long run on sentence which I am unsure of what it means: "but incomparability and lack of comprehensiveness in nest site selection was often stressed out " - why 12.5 m for the nest plot? Was this the standard size used and thus comparable to other studies? - Usually one doesn't mark nest trees so that possible predators don't create a search pattern. - Slightly arbitrary qualification of tree vitality - other more specific forestry terms or hardness tests? - Line 142-144: Does dry = dead? - Line 145-146: describe feeding signs? Of what? - Line 165: form = from. Which forest management plans? More information on the specific area surveyed, year, methods, ect. - Line 166: Basal area for each tree species per hectare? - Line 171: What were the differences? 'Floristic structure' is a bit of an odd term - Line 182: Explain the Rayleigh uniformity test and why it was chosen instead of a comparison to computer generated ordinal data? - Line 190-191: Where did the study plot data come from? What this from the 'Forest Management plan'? - General stats: Did you run correlation test for the NT or NP variables? You should first ascertain that the variables were uncorrelated with each other prior to further analysis. Line 229: Average entrance height Line 260-261: Species of trees? Line 282-283: Again if you are comparing average of averages I would not feel certain about this Line 285-286: Still not sure what feeding marks entail and why they are being measured Line 300: Unsure of what this sentence means Line 351-316: Did you measure or test for? This appears to be one of the main points of the study but the first time it is mentioned is in the discussion 4

Lines 316-325 are basically a literature review. This is the first paragraph of the discussion - a place in the paper where you should discuss your most important and critical findings instead of summarizing existing literature Lines 328-330: This statement suggests that either (1), or (2). I am not convinced either is true. Line 325-327: Unsure what this statement means. Lines 330-340: Again lacking a discussion of new findings Line 341-346: Messy and confusing dialogue. Line 347-350: Do not quote entire sentences from existing literature Line 375-376: Will basal measurements fully support the statement of tree dominance? There could be less trees of the species but if they are larger they will contribute more to the basal count. Typically dominance is a measure of individual numbers Line 339-408: The average of all trees including very small ones should not even be included in the paper - remove statistic and discussion. Actually entire paragraph can be removed as the adjusted average were NS Line 411-413: I don't see any support for this statement 5