Monitoring Report. Sclerocactus mesae-verdae Transplant Project



Similar documents
Mesa Verde Cactus Sclerocactus mesae-verdae. 5-Year Review Summary and Evaluation

runing & Orchard Renewal

Preserving Wild Ginseng in Minnesota

Identification and Prevention of Frost or Freeze Damage By Linda Reddick, Kingman Area Master Gardener

Public Comment Period Summary Report Four Corners Power Plant and Navajo Mine Energy Project. EXHIBIT H Notification Flier Distribution Database

STANDARDS FOR RANGELAND HEALTH ASSESSMENT FOR SAGEHEN ALLOTMENT #0208

Post-Wildfire Clean-Up and Response in Houston Toad Habitat Best Management Practices

Federal Research and Development in South Dakota

RARE PLANTS AND BOTANICALLY SIGNIFIGANT ASSEMBLAGES

Oak Trees BASIC GROWING REQUIREMENTS FOR YOUR

LIVING LANDS Helping Land Trusts Conserve Biodiversity

KINGMAN IS GROWING! Column

The Basics of Tree Pruning

Many Voices, Many Visions: Analyzing Contemporary Environmental Issues. Teacher s Masters California Education and the Environment Initiative

Pruning Fruit Trees. Develop strong tree structure. This should begin when trees are planted and continue each year thereafter.

National Interagency Aviation Council (NIAC) Phase III Strategy

ARIZONA GAME AND FISH DEPARTMENT HABITAT PARTNERSHIP PROGRAM HABITAT ENHANCEMENT AND WILDLIFE MANAGEMENT PROPOSAL PROJECT INFORMATION PROJECT FUNDING

FORESTED VEGETATION. forests by restoring forests at lower. Prevent invasive plants from establishing after disturbances

H-GAC Debris Workshop 2: Mitigating Your Hazards Handout 1 Public Outreach Debris Mitigation Strategies

TECHNICAL NOTES. Salvage Techniques for Saguaro Cacti, Barrel Cacti and Ocotillo. TN Plant Materials 9 1- Arizona September 2009

by Erik Lehnhoff, Walt Woolbaugh, and Lisa Rew

Experience Summary. KINA MURPHY, M.S. Ecologist / Community Planner 9 Stone Ridge Road, Santa Fe, NM Cell: Education / Training

Interactions between rodent borne diseases and climate, and the risks for public and animal health

THIRTYMILE ACCIDENT PREVENTION ACTION PLAN

Monitoring Riparian Areas With a Camera

Healthy Forests Resilient Water Supply Vibrant Economy. Ecological Restoration Institute

Drought Response Program: Draft Funding Criteria for Review and Comment

Forest Watershed Tree Thinning Restoration Effectiveness Monitoring in the Manzano Mountains of New Mexico

STATEMENT OF RON HUNTSINGER NATIONAL SCIENCE COORDINATOR BUREAU OF LAND MANAGEMENT U.S

March 17, Dear Mr. Sullins:

JUNIPER TREE NURSERY. Growing The Future Forest Today. A Promise We ve Been Keeping Since 1957.

The Feasibility of Chaparral Restoration on Type-converted Slopes MEGAN ENGEL KIMBERLYN WILLIAMS CHRISTOPHER MCDONALD JAN BEYERS

1 INTRODUCTION. Kayenta Complex Page 9 December 2011 Cumulative Hydrologic Impact Assessment

Multiple Species Conservation Program County of San Diego. A Case Study in Environmental Planning & The Economic Value of Open Space

Central Oregon Climate and how it relates to gardening

ENDANGERED AND THREATENED

The Greater Sage-Grouse:

Florida Native Plant Society

Colorado Natural Heritage Program

Rocky Mountain Wolf Recovery 2009 Interagency Annual Report

understanding Sustainable Landscaping & Tree Preservation Standards

Growth and development of. Trees

Questions and Answers: Scoping for Southwestern Willow Flycatcher Critical Habitat Proposal

Maintaining Cactus and Succulents

Hanford Site Rare Plant Monitoring Report for Calendar Year 2012

State Noxious Weed Laws, Lists, Regulations and Policies

APPENDIX B: COMMON AND SCIENTIFIC NAMES OF IDAHO SPECIES OF GREATEST CONSERVATION NEED.

Diagnosing Disorders of Trees

OVERVIEW ABOUT WBI ENERGY

U.S. Fish and Wildlife Service will invest $15 million for post-sandy cleanup and marsh restoration on Long Island

Ten Easy Ways to Kill a Tree

Construction Damage to Trees

Work Report for Sino-Italian Cooperation Project ( ) Application of Vallerani System Technology in Demonstration Forestation in Inner Mongolia

Dawn Reis Ecological Studies.

Extinction; Lecture-8

Patterns of Bat Fatality at Wind Development Facilities. Edward B. Arnett, Bat Conservation International

COLORADO PLATEAU COOPERATIVE ECOSYSTEM STUDIES UNIT. AMENDMENT THREE TO COOPERATIVE and JOINT VENTURE AGREEMENT. between NAVAJO NATION

Ruby River Grayling - Gravel Spawning Beds Monitoring Report January 2008

Avoiding Tree & Utility Conflicts

Increasing water availability through juniper control.

Submitted Electronically via erulemaking Portal to FWS-R5-ES

First Annual Centennial Strategy for. Yucca House National Monument

UPPER COLORADO AND SAN JUAN RIVER BASINS ENDANGERED FISH RECOVERY PROGRAMS

Communities, Biomes, and Ecosystems

SANTA BARBARA COUNTY COMPREHENSIVE PLAN LOMPOC AREA

Wausau and Marathon County Parks, Recreation, and Forestry Department Forestry Division 2015 Work Plan

Chapter 3 Communities, Biomes, and Ecosystems

Key Idea 2: Ecosystems

Biological control of walnut blight: screening of antagonistic bacteria for Xanthomonas arboricola pv. juglandis and evaluation of their efficacy

How To Understand And Care For An Elder Cornflower Cactus

Evergreen Carbon Capture - 2

King Fire Restoration Project, Eldorado National Forest, Placer and El Dorado Counties, Notice of intent to prepare an environmental impact statement.

Croft House Lodge Tree Removal and Building Relocation Mitigation Report. November 2010

How To Plan A Buffer Zone

COUNTY OF LOS ANGELES OAK TREE ORDINANCE

TFL 55 CHANGE MONITORING INVENTORY SAMPLE PLAN

Columbia River Project Water Use Plan. Monitoring Program Terms of Reference LOWER COLUMBIA RIVER FISH MANAGEMENT PLAN

Two Main Precautions Before You Begin Working

SECTION 3.2 CLIMATE AND PRECIPITATION

United States Department of the Interior

High Conservation Value Forests 3.1. Old Growth Forests. Management & Monitoring Framework

Pruning Deciduous Shade Trees

Addendum D. Nomination of Moody Wash ACEC

Integrated Pest Management

ANNUAL REPORT UNALIENATED CROWN LAND WEED CONTROL TASMAN-NELSON DISTRICT

Moving Forward: Agricultural Water Conservation, Productivity, and Water Transfers Workgroup

Jackson Hydroelectric Project (FERC Project No. 2157) Revised Study Plan 12: Northern Spotted Owl Surveys. Final Technical Report

3.3.3 Capelin (Mallotus villosus) in Subareas I and II (Northeast Arctic), excluding Division IIa west of 5 W (Barents Sea capelin)

ENVIRONMENTAL CHANGES

TREE NOTES. CALIFORNIA DEPARTMENT OF FORESTRY AND FIRE PROTECTION Arnold Schwarzenegger Governor State of California. Dale T.

Untreated (left) and treated (right) Sierra Nevada forests in Amador County, CA. Photos: Sierra Nevada Conservancy

PROPERTY TAX RELIEF PROGRAMS

STREAMFLOW RESTORATION PRIORITY AREAS

Environmental Review Process

Determining the relative resistance of selected Pinus species to fire damage

Chapter 1b - Priority Map Development

November 20, Hand Delivery. New Bedford Conservation Commission 133 William Street, Room 304 New Bedford, MA 02740

Urban and Community Forestry Agriculture & Natural Resources TIMELY INFORMATION Post Storm Tree Assessment; Guide to evaluating trees

Middle School and High Schools

Techniques and Tools for Monitoring Wildlife on Small Woodlands

Transcription:

Monitoring Report Sclerocactus mesae-verdae Transplant Project Northern Navajo Fairgrounds Shiprock, San Juan County, NM 28 By Daniela Roth, Botanist Navajo Natural Heritage Program Department of Fish & Wildlife P.O. Box 148 Window Rock, AZ 86515

INTRODUCTION On March 27, 21, Navajo Natural Heritage Program staff (Department of Fish & Wildlife) excavated 55 Mesa Verde Cacti (Sclerocactus mesae-verdae) from the southcentral portion of the proposed Northern Navajo Fairgrounds site located south of Shiprock, New Mexico, east of US HWY 491, and north of Navajo Route 36. The roots of the cacti were slightly trimmed to stimulate root growth and then dipped in a diluted Clorox solution in an effort to prevent bacterial infections. The cacti were then stored at the greenhouse of the Navajo Fish & Wildlife Department for two weeks to allow the roots to heal over. Only one cactus died during this period. On April 9 th, 21, we delineated 5 monitoring plots within the designated nondevelopment zone of the future fairgrounds. The monitoring plots were mapped and the boundaries were marked with rebar and wooden stakes. Monitoring plot location and size was determined by the presence of existing Mesa Verde Cacti. Naturally occurring cacti serve as a control and are monitored together with the transplanted cacti during annual monitoring efforts. METHODS On April 1, 21, 54 cacti were planted within the established monitoring plots. Eleven cacti were planted into plot 1, which also contained 11 naturally occurring cacti. Eight cacti were planted into plot 2, containing 4 naturally occurring cacti. Plot 3 received 8 cacti, containing 9 naturally occurring cacti. Plot 4 was planted with 13 cacti. It contained 9 naturally occurring cacti. Plot 5 was planted with 14 cacti, and contained 16 naturally occurring cacti. All together there were 49 naturally occurring cacti and 54 transplanted cacti. All plants were mapped, numbered and tagged. Monitoring takes place annually. Determined and recorded are plant vigor, reproductive status and diameter for each plant. Multi-stemmed cacti are counted as one plant but are measured individually for vigor, reproductive status and diameter. This baseline information is used to determine the success of the transplanting effort. RESULTS Annual monitoring in 28 took place on April 3. In 28, 17 naturally occurring and 19 transplanted cacti were found alive in the 5 monitoring plots (Figure 1). No new cacti were recruited into the population since 27 and two had died, both of which were naturally occurring cacti. Two naturally occurring cacti were not relocated in 28. Recruitment of cacti from the seedbank into the population remains low. In 22, 7 cacti were recruited into the population, 6 in 23, 1 in 24, 5 in 25 and 27 and none in 26 and 28. Five naturally occurring cacti have died between 25 and 28 and none of the transplanted cacti. Seventy-six percent of the naturally occurring cacti and sixty-five percent of the 54 transplanted cacti died between 21 and 24, the majority as a result of the drought of 22. In 28, all natural cacti and 89% of the transplanted cacti were in excellent health (Figure 2.). One transplanted cactus was rated in good condition and one in fair health. In 28 reproductive effort increased to its highest level since 21. Fifty-three percent of naturally occurring cacti were reproductive in 28 and 5% of the transplanted cacti (Figures 3 & 4, Table1). Since 23 only three of the cacti have measured above 4 cm in diameter (transplanted), most others remain in the 1. to 3.99 category. The average diameter fro naturally occurring cacti is smaller since cacti are continually recruited into

the population from seedlings. None of the transplanted cacti were below 2.cm in diameter by 28(Figure 5, Table 2). Originally, transplanted cacti had a larger proportion of juvenile, small diameter plants (<1.99cm) and a lower proportion of large diameter, mature plants (> 5.cm) than the naturally occurring cacti (Figure 6, Table 2). This trend continued into 22, after which there was a shift in diameter size classes from larger diameters towards smaller size classes. By 25, all naturally occurring cacti with a diameter above 3.cm were gone and only 26% of the transplanted cacti were larger than 3 cm in diameter. The small diameter size classes (< 3.cm) fared best among transplanted as well as naturally occurring cacti. CONCLUSION The drought of 21/22 combined with a subsequent insect attack had a severe impact on both naturally occurring Mesa Verde Cacti as well as transplanted cacti. This was apparent during the two monitoring seasons following the drought through unprecedented high mortality rates, very low reproductive effort, decreases in diameter and low vigor of surviving plants. Both transplanted and naturally occurring cacti were affected similarly, although large diameter plants had a higher mortality rate and therefore more naturally occurring cacti died. Large diameter plants were more susceptible to insect attacks than the smaller cacti. Mortality rates have dropped off since 23 and new plants continue to be recruited into the population through 27, although at a very low level. A very dry winter of 25/26 likely contributed to the lack of reproductive effort and recruitment in the spring of 26 as well as the lower vigor among transplanted cacti. By 27 and 28 vigor increased and was rated excellent for all naturally occurring plants and most transplanted cacti. Reproductive effort increased substantially in 28, likely due to increased rainfall and the maturation of juvenile plants.

6 5 Number of Plants 4 3 2 1 21 22 23 24 25 26 27 28 Year Natural Transplants Figure 1. Total number of transplanted and naturally occurring Sclerocactus mesae-verdae plants from 21 to 28 in 5 monitoring plots at the future Northern Navajo Fairgrounds near Shiprock, NM. Vigor 1% 9% 8% Percent of Total 7% 6% 5% 4% 3% 2% 1% % 21 21 22 22 23 23 24 24 25 25 26 26 27 27 28 28 Natural Transplants Natural Transplants Natural Transplants Natural Transplants Natural Transplants Natural Transplants Natural Transplants Natural Transplants Excellent Good Fair Poor Figure 2. Percent of Sclerocactus mesae-verdae plants belonging to each of 4 vigor classes from 21 to 28 for transplanted and naturally occurring cacti in 5 monitoring plots at the future Northern Navajo Fairgrounds near Shiprock, NM.

Total Reproductive Effort Number of Reproductive Structures 12 1 8 6 4 2 21 22 23 24 25 26 27 28 Year Natural Transplants Figure 3. Number of reproductive structures found on transplanted and naturally occurring Sclerocactus mesae-verdae plants in 5 monitoring plots at the future Northern Navajo Fairgrounds near Shiprock, NM. Percent Reproduction 8 7 Percent of Plants 6 5 4 3 2 1 21 22 23 24 25 26 27 28 Year Natural Transplants Figure 4. Percent of the total number of transplanted and naturally occurring Sclerocactus mesae-verdae plants reproducing in 5 monitoring plots at the future Northern Navajo Fairgrounds near Shiprock, NM.

Average Diameter Average Diameter (cm) 4 3.5 3 2.5 2 1.5 1.5 21 22 23 24 25 26 27 28 Year Natural Transplants Figure 5. Average diameter of transplanted and naturally occurring Sclerocactus mesaeverdae plants in 5 monitoring plots at the future Northern Navajo Fairgrounds near Shiprock, NM. Diameter Size Classes 3 25 Number of Palnts 2 15 1 5 21 21 22 22 23 23 24 24 25 25 26 26 27 27 28 28 Transplants Natural Transplants Natural Transplants Natural Transplants Natural Transplants Natural Transplants Natural Transplants Natural Transplants Natural -.99cm 1-1.99cm 2-2.99cm 3-3.99cm 4-4.99cm > 5.cm Figure 6. Diameter size classes for transplanted and naturally occurring Sclerocactus mesae-verdae plants in 5 monitoring plots at the future Northern Navajo Fairgrounds near Shiprock, NM.

Table 1. Reproductive effort among transplanted and naturally occurring Sclerocactus mesaeverdae plants in 5 monitoring plots at the future Northern Navajo Fairgrounds near Shiprock, NM. Transplants 21 22 23 24 25 26 27 28 Buds 85 1 Flowers 4 5 2 2 Immature Fruit 5 7 9 Mature Fruit 1 4 7 Aborted Flowers 1 4 2 1 Total 89 2 18 12 19 Natural 21 22 23 24 25 26 27 28 Buds 14 11 Flowers 3 4 Immature Fruit 1 14 Mature Fruit 1 3 6 Aborted Flowers 1 1 Total 14 11 2 4 4 24 Table 2. Size class distribution of natural and transplanted Sclerocactus mesae-verdae plants in 5 monitoring plots at the future Northern Navajo Fairgrounds near Shiprock, NM. Transplants 21 22 23 24 25 26 27 28 -.99cm 1 1 1 1 1 1-1.99cm 2 24 8 8 6 8 2 2-2.99cm 12 15 9 6 1 9 8 7 3-3.99cm 9 9 5 7 5 3 1 8 4-4.99cm 12 2 1 1 1 3 > 5.cm 5 1 Total 58 52 23 23 23 21 21 18 Natural 21 22 23 24 25 26 27 28 -.99cm 1 3 5 3 5 1 1 1-1.99cm 1 14 5 7 14 14 2 11 2-2.99cm 18 19 3 4 4 3 1 18 3-3.99cm 3 3 2 1 1 1 4-4.99cm 6 14 2 > 5.cm 15 1 Total 53 6 15 17 21 22 32 31

REFERENCES Benson, L. 1982. The Cacti of the United States and Canada. Stanford University Press, Stanford, CA. Heil, K., and J.M. Porter. 1994. Sclerocactus (Cactaceae): A Revision. Haseltonia No. 2: 2-46. Ladyman, J. 24. Status Assessment Report for Sclerocactus mesae-verdae (Mesa Verde Cactus). Prepared for: The Navajo Natural Heritage Program, Window Rock, AZ. http://nnhp.navajofishandwildlife.org/docs_reps.htm New Mexico Rare Plant Technical Council. 1999. New Mexico Rare Plants. Albuquerque, NM: New Mexico Rare Plants Home Page. http://nmrareplants.unm.edu (Latest update: 18 January 26). Roth, D. 28. Species Account for Mesa Verde Cactus. In: Mikesic, D. & D. Roth. 28. Navajo Nation Endangered Species List Species Accounts. Navajo Natural Heritage Program, Department of Fish & Wildlife, Window Rock, AZ. http://nnhp.navajofishandwildlife.org/ Roth, D. 21 27. Monitoring Report. Sclerocactus mesae verdae Transplant Project, Northern Navajo Fairgrounds, Shiprock, San Juan County, NM. Unpublished annual update prepared for the Navajo Natural Heritage Program, Window Rock, AZ. Spackman, S., B. Jennings, J. Coles, C. Dawson, M. Minton, A. Kratz, and C. Spurrier. 1997. Colorado Rare Plant Field Guide. Prepared for the Bureau of Land Management, the U.S. Forest Service and the U.S. Fish & Wildlife Service by the Colorado Natural Heritage Program. http://www.cnhp.colostate.edu/rareplants/cover.html USDI Bureau of Land Management. 1995. The Farmington District Endangered, Threatened, and Sensitive Plant Field Guide. Prepared by Ecosphere Environmental Services, Inc., Farmington, NM. U.S. Fish & Wildlife Service. 1984. Mesa Verde Cactus (Sclerocactus mesae-verdae) recovery plan. U.S. Fish & Wildlife Service, New Mexico Ecological Services Field Office, Albuquerque, NM.