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溶解有机碳输出及土地管理决策对不列颠哥伦比亚省沿海以花旗松为主的景观流域尺度森林碳预算的历史影响。

Historical effects of dissolved organic carbon export and land management decisions on the watershed-scale forest carbon budget of a coastal British Columbia Douglas-fir-dominated landscape.

作者信息

Smiley B P, Trofymow J A

机构信息

Natural Resources Canada, Canadian Forest Service, 506 West Burnside Road, Victoria, BC, V8Z 1M5, Canada.

Biology Department, University of Victoria, Victoria, BC, V8W 3R4, Canada.

出版信息

Carbon Balance Manag. 2017 Dec;12(1):15. doi: 10.1186/s13021-017-0083-z. Epub 2017 Jul 14.

DOI:10.1186/s13021-017-0083-z
PMID:28707260
原文链接:https://pmc.ncbi.nlm.nih.gov/articles/PMC5509570/
Abstract

BACKGROUND

To address how natural disturbance, forest harvest, and deforestation from reservoir creation affect landscape-level carbon (C) budgets, a retrospective C budget for the 8500 ha Sooke Lake Watershed (SLW) from 1911 to 2012 was developed using historical spatial inventory and disturbance data. To simulate forest C dynamics, data was input into a spatially-explicit version of the Carbon Budget Model-Canadian Forest Sector (CBM-CFS3). Transfers of terrestrial C to inland aquatic environments need to be considered to better capture the watershed scale C balance. Using dissolved organic C (DOC) and stream flow measurements from three SLW catchments, DOC load into the reservoir was derived for a 17-year period. C stocks and stock changes between a baseline and two alternative management scenarios were compared to understand the relative impact of successive reservoir expansions and sustained harvest activity over the 100-year period.

RESULTS

Dissolved organic C flux for the three catchments ranged from 0.017 to 0.057 Mg C ha year. Constraining CBM-CFS3 to observed DOC loads required parameterization of humified soil C losses of 2.5, 5.5, and 6.5%. Scaled to the watershed and assuming none of the exported terrestrial DOC was respired to CO, we hypothesize that over 100 years up to 30,657 Mg C may have been available for sequestration in sediment. By 2012, deforestation due to reservoir creation/expansion resulted in the watershed forest lands sequestering 14 Mg C ha less than without reservoir expansion. Sustained harvest activity had a substantially greater impact, reducing forest C stores by 93 Mg C ha by 2012. However approximately half of the C exported as merchantable wood during logging (~176,000 Mg C) may remain in harvested wood products, reducing the cumulative impact of forestry activity from 93 to 71 Mg C ha.

CONCLUSIONS

Dissolved organic C flux from temperate forest ecosystems is a small but persistent C flux which may have long term implications for C storage in inland aquatic systems. This is a first step integrating fluvial transport of C into a forest carbon model by parameterizing DOC flux from soil C pools. While deforestation related to successive reservoir expansions did impact the watershed-scale C budget, over multi-decadal time periods, sustained harvest activity was more influential.

摘要

背景

为了研究自然干扰、森林采伐以及水库建设导致的森林砍伐如何影响景观尺度的碳(C)收支,利用历史空间清查和干扰数据,编制了1911年至2012年期间8500公顷的苏克湖流域(SLW)的回顾性碳收支。为了模拟森林碳动态,将数据输入到碳收支模型-加拿大森林部门(CBM-CFS3)的空间明确版本中。为了更好地掌握流域尺度的碳平衡,需要考虑陆地碳向内陆水生环境的转移。利用来自SLW三个集水区的溶解有机碳(DOC)和流量测量数据,得出了17年期间进入水库的DOC负荷。比较了基线和两种替代管理情景之间的碳储量和储量变化,以了解在100年期间连续水库扩建和持续采伐活动的相对影响。

结果

三个集水区的溶解有机碳通量范围为0.017至0.057 Mg C ha⁻¹ year⁻¹。将CBM-CFS3限制在观测到的DOC负荷范围内,需要对腐殖化土壤碳损失进行参数化,分别为2.5%、5.5%和6.5%。按流域比例缩放,并假设输出的陆地DOC没有呼吸转化为CO₂,我们推测在100年内,高达30657 Mg C的碳可能可用于沉积物中的封存。到2012年,由于水库建设/扩建导致的森林砍伐使流域林地的碳固存比没有水库扩建时少14 Mg C ha⁻¹。持续的采伐活动产生了更大的影响,到2012年,森林碳储量减少了93 Mg C ha⁻¹。然而,在采伐期间作为商品木材输出的碳中,约有一半(~176000 Mg C)可能保留在采伐的木材产品中,从而将林业活动的累积影响从93 Mg C ha⁻¹降至71 Mg C ha⁻¹。

结论

温带森林生态系统中的溶解有机碳通量虽小但持续存在,可能对内陆水生系统中的碳储存产生长期影响。这是通过对土壤碳库中的DOC通量进行参数化,将河流碳输运纳入森林碳模型的第一步。虽然与连续水库扩建相关的森林砍伐确实影响了流域尺度的碳收支,但在几十年的时间里,持续的采伐活动影响更大。

https://cdn.ncbi.nlm.nih.gov/pmc/blobs/17bc/5509570/aa65e03cf457/13021_2017_83_Fig9_HTML.jpg
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https://cdn.ncbi.nlm.nih.gov/pmc/blobs/17bc/5509570/dbd226dfd83b/13021_2017_83_Fig8_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/17bc/5509570/aa65e03cf457/13021_2017_83_Fig9_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/17bc/5509570/71f23723ea27/13021_2017_83_Fig1_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/17bc/5509570/c3f526e43f40/13021_2017_83_Fig2_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/17bc/5509570/39c18bea1d4c/13021_2017_83_Fig3_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/17bc/5509570/7a92dda96617/13021_2017_83_Fig4_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/17bc/5509570/bf1d3380df97/13021_2017_83_Fig5_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/17bc/5509570/9c5aa804880d/13021_2017_83_Fig6_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/17bc/5509570/137e08822d91/13021_2017_83_Fig7_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/17bc/5509570/dbd226dfd83b/13021_2017_83_Fig8_HTML.jpg
https://cdn.ncbi.nlm.nih.gov/pmc/blobs/17bc/5509570/aa65e03cf457/13021_2017_83_Fig9_HTML.jpg

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