Carbon stored in live ponderosa pines in the Sierra Nevada will not return to pre-drought (2012) levels during the 21st century due to bark beetle outbreaks

被引:3
作者
Robbins, Zachary J. [1 ,2 ]
Xu, Chonggang [1 ]
Jonko, Alex [1 ]
Chitra-Tarak, Rutuja [1 ]
Fettig, Christopher J. [3 ]
Costanza, Jennifer [4 ]
Mortenson, Leif A. [3 ]
Aukema, Brian H. [5 ]
Kueppers, Lara M. [6 ]
Scheller, Robert M. [2 ]
机构
[1] Los Alamos Natl Lab, Earth & Environm Sci Div, Los Alamos, NM 87545 USA
[2] North Carolina State Univ, Dept Forestry & Environm Resources, Raleigh, NC 27607 USA
[3] USDA Forest Serv, Pacific Southwest Res Stn, Davis, CA USA
[4] USDA Forest Serv, Southern Res Stn, Res Triangle Pk, NC USA
[5] Univ Minnesota, Dept Entomol, St Paul, MN USA
[6] Univ Calif Berkeley, Energy & Resources Grp, Berkeley, CA USA
关键词
bark beetles; climate change; Dendroctonus brevicomis; forest disturbance; forest recovery; Pinus ponderosa; tree mortality; Sierra Nevada; CLIMATE-CHANGE; UNITED-STATES; WESTERN; CALIFORNIA; DISTURBANCES; DYNAMICS; FORESTS;
D O I
10.3389/fenvs.2023.1112756
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Outbreaks of several bark beetle species can develop rapidly in response to drought and may result in large transfers of carbon (C) stored in live trees to C stored in dead trees (10s of Tg C yr(-1) in the western U.S. alone), which over time will be released back to the atmosphere. The western pine beetle (WPB) outbreak incited by the 2012-2015 mega-drought in the Sierra Nevada, California, U.S., could portend more frequent and/or severe bark beetle outbreaks as the temperature warms and drought frequency and intensity increase in the future. However, changes in the frequency and/or severity (resultant levels of host tree mortality) of beetle outbreaks are difficult to predict as outbreaks are complex with non-linear and eruptive processes primarily driven by interactions among beetle populations, the demography of hosts and other tree species, and climate and weather. Using an insect phenology and tree defense model, we projected the future likelihood of WPB outbreaks in the Sierra Nevada with climate drivers from different Earth System Models. Our goal was to understand how host (ponderosa pine, PIPO) recovery and future warming and drought affect the frequency and severity of WPB outbreaks and their C consequences. Our projections suggested that by 2100 the C stored in live PIPO (mean: 1.98 kg C m(-2,) 95% CI: 1.74-2.21 kg C m(-2)) will not return to levels that occurred before the 2012-2015 drought (2012: similar to 2.30 kg C m(-2)) due to future WPB outbreaks. However, differences in climate models indicate a wide range of possible WPB outbreak frequencies and severities. Our results suggest that total plot basal area is the most significant factor in the mortality rate of PIPO by WPB in any given year, followed by drought severity and temperature. High levels of host basal area, higher temperature, and extreme drought all contribute to the frequency and severity of future WPB outbreaks. While PIPO basal area may decline under increased drought and warming, limiting high-stand basal area (>60 m(2) ha(-1)) may reduce the severity of future WPB outbreaks in the Sierra Nevada.
引用
收藏
页数:13
相关论文
共 61 条
  • [1] A comparison of statistical downscaling methods suited for wildfire applications
    Abatzoglou, John T.
    Brown, Timothy J.
    [J]. INTERNATIONAL JOURNAL OF CLIMATOLOGY, 2012, 32 (05) : 772 - 780
  • [2] Adams M. B., 2004, NEGTR321 US DEP AGR
  • [3] Tree mortality from drought, insects, and their interactions in a changing climate
    Anderegg, William R. L.
    Hicke, Jeffrey A.
    Fisher, Rosie A.
    Allen, Craig D.
    Aukema, Juliann
    Bentz, Barbara
    Hood, Sharon
    Lichstein, Jeremy W.
    Macalady, Alison K.
    McDowell, Nate
    Pan, Yude
    Raffa, Kenneth
    Sala, Anna
    Shaw, John D.
    Stephenson, Nathan L.
    Tague, Christina
    Zeppel, Melanie
    [J]. NEW PHYTOLOGIST, 2015, 208 (03) : 674 - 683
  • [4] Bechtold WA, 2005, ENHANCED FOREST INVE, V80
  • [5] Climate Change and Bark Beetles of the Western United States and Canada: Direct and Indirect Effects
    Bentz, Barbara J.
    Regniere, Jacques
    Fettig, Christopher J.
    Hansen, E. Matthew
    Hayes, Jane L.
    Hicke, Jeffrey A.
    Kelsey, Rick G.
    Negron, Jose F.
    Seybold, Steven J.
    [J]. BIOSCIENCE, 2010, 60 (08) : 602 - 613
  • [6] Bentz BJ., 2015, BARK BEETLES BIOL EC, P533, DOI [10.1016/B978-0-12-417156-5.00013-7, DOI 10.1016/B978-0-12-417156-5.00013-7]
  • [7] Biomass stocks in California's fire-prone forests: mismatch in ecology and policy
    Bernal, Alexis A.
    Stephens, Scott L.
    Collins, Brandon M.
    Battles, John J.
    [J]. ENVIRONMENTAL RESEARCH LETTERS, 2022, 17 (04):
  • [8] Buluc L., 2017, SYNOPSIS PRESENTATIO
  • [9] Capturing functional strategies and compositional dynamics in vegetation demographic models
    Buotte, Polly C.
    Koven, Charles D.
    Xu, Chonggang
    Shuman, Jacquelyn K.
    Goulden, Michael L.
    Levis, Samuel
    Katz, Jessica
    Ding, Junyan
    Ma, Wu
    Robbins, Zachary
    Kueppers, Lara M.
    [J]. BIOGEOSCIENCES, 2021, 18 (14) : 4473 - 4490
  • [10] Changing forest structure across the landscape of the Sierra Nevada, CA, USA, since the 1930s
    Dolanc, Christopher R.
    Safford, Hugh D.
    Thorne, James H.
    Dobrowski, Solomon Z.
    [J]. ECOSPHERE, 2014, 5 (08):