By: Paul Pellissier, Andrew Ouimette, Lucie Lepine

Slides:



Advertisements
Similar presentations
Site and Stocking and Other Related Measurements.
Advertisements

Why gap filling isn’t always easy Andrew Richardson University of New Hampshire Jena Gap Filling Workshop September 2006.
Do In and Post-Season Plant-Based Measurements Predict Corn Performance and/ or Residual Soil Nitrate? Patrick J. Forrestal, R. Kratochvil, J.J Meisinger.
Comprehensive evaluation of Leaf Area Index estimated by several method Comprehensive evaluation of Leaf Area Index estimated by several method ― LAI-2000,
Lecture 7 Forestry 3218 Forest Mensuration II Lecture 7 Forest Inventories Avery and Burkhart Chapter 9.
Intro to Statistics for the Behavioral Sciences PSYC 1900
9/17/071 Community Properties Reading assignment: Chapter 9 in GSF.
Questions How do different methods of calculating LAI compare? Does varying Leaf mass per area (LMA) with height affect LAI estimates? LAI can be calculated.
Introduction Subalpine meadows play a crucial role in species diversity, supporting many endangered species of plant and wildlife. Subalpine meadows play.
Relationships Among Variables
Accuracy Assessment. 2 Because it is not practical to test every pixel in the classification image, a representative sample of reference points in the.
Statistical Methods For Engineers ChE 477 (UO Lab) Larry Baxter & Stan Harding Brigham Young University.
Examination of Tropical Forest Canopy Profiles Using Field Data and Remotely Sensed Imagery Michael Palace 1, Michael Keller 1,2, Bobby Braswell 1, Stephen.
Precipitation Effects on Tree Ring Width for Ulmus americana L
 For AC ramp breakdown testing a Phenix AC Dielectric Test Set, Type 600C was used with a custom built test cell.  The test cell used mushroom electrodes.
Quantitative Estimates of Biomass and Forest Structure in Coastal Temperate Rainforests Derived from Multi-return Airborne Lidar Marc G. Kramer 1 and Michael.
Predictors of tree growth in damar agroforests Grégoire Vincent * and Hubert de Foresta Introduction Damar agroforest (Lampung, Sumatra) are multi-species,
Introduction To describe the dynamics of the global carbon cycle requires an accurate determination of the spatial and temporal distribution of photosynthetic.
How Do Forests, Agriculture and Residential Neighborhoods Interact with Climate? Andrew Ouimette, Lucie Lepine, Mary Martin, Scott Ollinger Earth Systems.
Field Measurements of Leaf Mass Area (LMA) in Support of Remote Sensing Studies of a Pacific Northwest Old Growth Forest Canopy Katie Berger (UMASS-Amherst)
Development of Vegetation Indices as Economic Thresholds for Control of Defoliating Insects of Soybean James BoardVijay MakaRandy PriceDina KnightMatthew.
How Do Forests, Agriculture and Residential Neighborhoods Interact with Climate? Andrew Ouimette, Lucie Lepine, Mary Martin, Scott Ollinger Earth Systems.
LiDAR Remote Sensing of Forest Vegetation Ryan Anderson, Bruce Cook, and Paul Bolstad University of Minnesota.
Goal: to understand carbon dynamics in montane forest regions by developing new methods for estimating carbon exchange at local to regional scales. Activities:
Spectral Reflectance Features Related to Foliar Nitrogen in Forests and their Implications for Broad-Scale Nitrogen Mapping Lucie C. Lepine, Scott V. Ollinger,
Examination of Canopy Disturbance in Logged Forests in the Brazilian Amazon using IKONOS Imagery Michael Palace 1, Michael Keller 1,2, Bobby Braswell 1,
Land-Climate Interactions Across 4 Land Cover Types in New Hampshire Latent and sensible heat “Sweating” Greenhouse Gases Longwave Radiation Albedo “Breathing”“Reflectivity”
Citation: Richardson, J. J, L.M. Moskal, S. Kim, Estimating Urban Forest Leaf Area Index (LAI) from aerial LiDAR. Factsheet # 5. Remote Sensing and.
Updated Cover Type Map of Cloquet Forestry Center For Continuous Forest Inventory.
Above and Below ground decomposition of leaf litter Sukhpreet Sandhu.
DEFINITION LEAF AREA INDEX is defined as one half the total foliage
Effects of Word Concreteness and Spacing on EFL Vocabulary Acquisition 吴翼飞 (南京工业大学,外国语言文学学院,江苏 南京211816) Introduction Vocabulary acquisition is of great.
Statistics Terminology. What is statistics? The science of conducting studies to collect, organize, summarize, analyze, and draw conclusions from data.
Stats Methods at IC Lecture 3: Regression.
Factsheet # 27 Canopy Structure From Aerial and Terrestrial LiDAR
and Other Related Measurements
Factsheet # 17 Understanding multiscale dynamics of landscape change through the application of remote sensing & GIS Estimating Tree Species Diversity.
Using vegetation indices (NDVI) to study vegetation
Assessing the climate impacts of land cover and land management using an eddy flux tower cluster in New England Earth Systems Research Center Institute.
Cases and controls A case is an individual with a disease, whose location can be represented by a point on the map (red dot). In this table we examine.
NDVI Active Sensors in Sugarbeet Production for In-Season and Whole Rotation Nitrogen Management.
College of Agriculture, Fisheries and Forestry.
Contact: Tel.: Exploring the influence of canopy structure on the link between canopy nitrogen concentration.
3-PG The Use of Physiological Principles in Predicting Forest Growth
Factsheet # 2 Leaf Area Index (LAI) from Aerial & Terrestrial LiDAR
Comparing Three or More Means
PCB 3043L - General Ecology Data Analysis.
Factsheet # 21 Understanding multiscale dynamics of landscape change through the application of remote sensing & GIS Quantifying Vertical and Horizontal.
Height and Pressure Test for Improving Spray Application
Accuracy and Precision
Understanding Standards Event Higher Statistics Award
Business and Management Research
Accuracy and Precision
Figure 1. Spatial distribution of pinyon-juniper and ponderosa pine forests is shown for the southwestern United States. Red dots indicate location of.
E.V. Lukina, K.W. Freeman,K.J. Wynn, W.E. Thomason, G.V. Johnson,
A Comparison of Riparian Vegetation Structures
Significant Figures The significant figures of a (measured or calculated) quantity are the meaningful digits in it. There are conventions which you should.
2. Stratified Random Sampling.
Gerald Dyer, Jr., MPH October 20, 2016
By: Paul A. Pellissier, Scott V. Ollinger, Lucie C. Lepine
Zaixing Zhou, Scott V. Ollinger, Lucie Lepine
A Comparison of Forest Biodiversity Metrics Using Field Measurements and Aircraft Remote Sensing Kaitlyn Baillargeon Scott Ollinger,
Prediction and Accuracy
Sources of Variability in Canopy Spectra and the Convergent Properties of Plants Funding From: S.V. Ollinger, L. Lepine, H. Wicklein, F. Sullivan, M. Day.
Spectral changes with leaf aging in Amazon caatinga
CHAPTER – 1.2 UNCERTAINTIES IN MEASUREMENTS.
Evaluating the Ability to Derive Estimates of Biodiversity from Remote Sensing Kaitlyn Baillargeon Scott Ollinger, Andrew Ouimette,
Tina Nguyen Vegetation Ecology Summer 2018
The effects of Canopy Cover on Herbaceous Vegetation
CHAPTER – 1.2 UNCERTAINTIES IN MEASUREMENTS.
Presentation transcript:

By: Paul Pellissier, Andrew Ouimette, Lucie Lepine Economic but Effective: Camera Point Method Provides Robust Estimation of Leaf Area Index in Northern Forests By: Paul Pellissier, Andrew Ouimette, Lucie Lepine --Abstract-- --Results-- Figure 3: Site location within New Hampshire. Bartlett Experimental Forest Leaf Area Index (LAI) is a central, but difficult to measure parameter crucial in the estimation of many ecosystem functions. This study proposes a new method that has proven to be a better at estimating LAI in northern forests than existing methods. --Methods-- Striving Towards Accurate LAI: For each plot, LAI was calculated over the entire hectare by varying the number of camera points used in the calculation from 135 to 1230. The results are shown in figure 5. Here we see that as the sample size increases the variance around the mean LAI value decreases. Additionally, there seems to be an asymptotic relationship between the gained accuracy in LAI and the number of camera points necessary to produce this gain. This relationship suggests a threshold near 500 camera points past which estimate accuracy increases only slightly relative to the effort needed to affect this change. This threshold value may prove important in future applications of this technique. Site Description: This study was conducted at the Bartlett Experimental Forest, located within the White Mountain National Forest near Bartlett, New Hampshire (44⁰03’ N, 71⁰17’ W)(figure 3). The experimental forest was established in 1931 for the study of ecology and forest management practices. Four, one hectare plots were established and selected to represent a gradient of species composition ranging from broad leafed deciduous to coniferous evergreen dominated stands. Stand age at all plots was between 75 and 100 years old. --Introduction-- What is Leaf Area Index? Leaf Area Index (LAI) is the ratio of leaf area (m2) per unit ground area (m2). It can also be thought of the number of leaf layers above a horizontal ground surface, with zero representing bare ground. Due to the pivotal role that leaves play in the Earth system, LAI is a central, but difficult to measure parameter crucial in the estimation of many ecosystem functions. These functions include: gross primary production, evapotranspiration, microclimate, nutrient dynamics, herbivory/food webs, as well as many others (Asner et al., 2003) . The importance of obtaining accurate measurements of LAI is compounded when working at larger scales. In this light, the relative inability to accurately estimate LAI represents a weakness for many ecosystem and climate models. The Camera Point Method: Camera point method has proven to be a simple and reliable way to assess forest canopy height profiles (Aber ,1979; Smith and Martin, 2000) (figure 2). The method involves a standard SLR camera equipped with a telephoto lens and a gridded eyepiece. Mounting the camera on a Field Survey: Figure 4: Plot layout with 8m grid superimposed on the larger 16m grid. At each plot a survey grid was established on a sixteen meter grid interval. One corner was further divided at eight meter intervals (figure 4). The sixteen meter interval was chosen for use in remote sensing analysis (not shown). At each intersection within the survey grid a set of fifteen camera point observations were made, one for each intersection in the optical quadrat (figure 1). For each observation, location, species, and height of the leaf were recorded. Additionally, if the quadrat intersection (camera point) landed on a branch, trunk, or on open sky it was recorded as such. Using this sampling method produced a total of 1230 camera points per plot. tripod, the lens is pointed straight up and acts as a rangefinder, while the grid on the viewfinder serves as an optical quadrat. Focusing the lens on the leaf which is covered by each quadrat intersection, the observer is able to identify the species of leaf and the height above the lens mount at which the leaf resides (figure 1). Leaves that are sighted higher in the canopy are given more weight in analysis, due to the fact that they tend to be systematically obscured by lower leaves. The true value of this technique lies in the versatility of the data collected. While rather basic, the data produced from camera point surveys are useful in the estimation of a number of ecosystem parameters. Many of these parameters are otherwise difficult or costly to determine and therefore underrepresented in the literature. Figure 1: A forest canopy as seen through the viewfinder. Figure 5: Normalized LAI values of four forested plots calculated with different numbers of camera points. Note the accuracy gained through the inclusion of more camera points. In order to evaluate the effectiveness of this technique, LAI values produce by three additional methods (Li-COR’s LAI 2000,Hemispherical photography, and Litterfall estimation) were compared to those of camera point for each plot. Furthermore, the mean LAI and variance within of the existing methods was also calculated (table 1). For all plots studied, the camera point LAI was well within the variance of the excepted methods and more often then not, offered a better prediction the mean value than any of the existing methods. Table 1: LAI method comparison between three professionally excepted methods and the camera point method. Mean and variance of the existing methods are also shown. Note that for all plots camera point LAI values are with the variance and in three of the four plots best predicts the excepted mean. * indicates values not included in mean and variance calculation. Data Analysis: Once collected the plot level data were binned by height, in two meter increments, and by species. An estimate of LAI and vertical distribution of foliage was then calculated according to the equation, y=ln(Nh1/Nh2) where y is LAI, h is the region of the canopy involved (in this case between two heights h1 and h2) and N is the is number of camera points sighted above a respective height (Aber 1979). For example, if we were to measure the whole canopy, H1 would be zero and H2 would be the top of the canopy. Nh1 would then be the number of camera points that surveyed a leaf and Nh2 would be how many camera point hit open sky. Using the same logic, segmenting the canopy into intervals and calculating the LAI for each interval produces an estimate of the vertical distribution of foliage throughout the canopy. The camera point method was previously thought to be a poor estimate of LAI due limitations inherent in the equation above. These limits include (1) the relationship that the sample size has with the total possible LAI, and (2) the assumption that leaves are randomly distributed in the horizontal direction. Limitation 1 can be dealt with by simply increasing the sample size to a number such that the maximum predictable LAI is greater than the actual LAI of the forest in question. Additionally, increasing the intensity of sampling is also likely to better represent non random patterns in leaf distribution such as also canopy gap fraction and leaf clumping. Existing LAI Method’s Predictions Plot LAI-2000 Hemiview Litterfall Mean Variance Camera Point 14Z 4.90 2.63 1.62 3.05 2.82 3.09 B2 4.87 2.56 3.29 3.57 1.40 2.95 32AF 4.07 1.79 3.46 3.11 1.39 2.99 32P 10.9* 2.48 3.41 0.43 2.66 Future Efforts: As this was conducted as a pilot study, further efforts will concentrate on surveying more plots. These plots should include near monocultures of both broad and needle leaved species as well as highly mixed stands. Additional energy will also focus on the further development of the number of camera points to accuracy threshold value and overall method development. Figure 2: An example of a canopy height profile produced from camera point sampling References Cited: Aber, John D. 1979. "A Method for estimating foliage-height profiles in broad-leaved forests." Journal Of Ecology 67, no. 1: 35. Asner, Gregory P., Jonathan M. O. Scurlock, and Jeffrey A. Hicke. 2003. "Global synthesis of leaf area index observations: implications for ecological and remote sensing studies." Global Ecology & Biogeography 12, no. 3: 191-205. Smith, Marie-Louise, and Mary E. Martin. 2001. "A plot-based method for rapid estimation of forest canopy chemistry."Canadian Journal Of Forest Research 31, no. 3: 549 Prepared for the 2012 University of New Hampshire Undergraduate Research Conference