H. Keith, Andrew Macintosh, B. Mackey, Michael H. Smith
{"title":"Forests","authors":"H. Keith, Andrew Macintosh, B. Mackey, Michael H. Smith","doi":"10.3368/er.10.1.82","DOIUrl":null,"url":null,"abstract":"In 1990, the U.S. Forest Service began a fouryear project to rehabilitate and expand recreational areas at Lost Lake, an area that has been a campground since 1900. Located just east of the Cascade Range crestline at 957 m above sea level, the project area receives 406 cm (160 inches) of precipitation a year, usually in the form of snow. The prevalent vegetation can be described as belonging to the Pacific silver fir (Abies) plant community. The project objective calls for building or reconstructing 133 campsites and 32 day-use sites along with over 4.8 km of roadway. Revegetation is integrated into the construction schedule since the area is accessible only from May through October. Our revegetation goals are 1) to minimize the area disturbed by construction and to salvage as many plants as possible within those areas; 2) to replant all disturbed areas using propagules collected on-site or from adjacent clearcuts; and 3) to protect the integrity of the identified plant subcommunities. Using a classification system developed in The Plant Association and Management Guide for the Pacific Silver Fir Zone (Hemstrom et al 1986), we identified four distinct plant sub-communities within the project area ranging from hydric to xeric. Data about vegetation, environment, and soil characteristics helped us develop a site plan, vegetation management plan, and revegetation specifications. We also used plant succession field data collected from adjacent clearcuts to determine the desired species composition and spacing for replanting. We planned all the work for this multi-year project by preparing revegetation specifications and requirements in the construction contract. Service crews, temporary employees and volunteers were then trained to carry out plant salvage, seed collection and propagation tasks. Each year, in the early spring before road construction begins, workers salvage most plant materials within the construction zone. They dig 10 to 15.25-cm-thick mats of pioneer grasses/forbs and transplant them directly into high-impact areas like","PeriodicalId":105419,"journal":{"name":"Restoration & Management Notes","volume":"24 1","pages":"0"},"PeriodicalIF":0.0000,"publicationDate":"2021-10-28","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Restoration & Management Notes","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.3368/er.10.1.82","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 0
Abstract
In 1990, the U.S. Forest Service began a fouryear project to rehabilitate and expand recreational areas at Lost Lake, an area that has been a campground since 1900. Located just east of the Cascade Range crestline at 957 m above sea level, the project area receives 406 cm (160 inches) of precipitation a year, usually in the form of snow. The prevalent vegetation can be described as belonging to the Pacific silver fir (Abies) plant community. The project objective calls for building or reconstructing 133 campsites and 32 day-use sites along with over 4.8 km of roadway. Revegetation is integrated into the construction schedule since the area is accessible only from May through October. Our revegetation goals are 1) to minimize the area disturbed by construction and to salvage as many plants as possible within those areas; 2) to replant all disturbed areas using propagules collected on-site or from adjacent clearcuts; and 3) to protect the integrity of the identified plant subcommunities. Using a classification system developed in The Plant Association and Management Guide for the Pacific Silver Fir Zone (Hemstrom et al 1986), we identified four distinct plant sub-communities within the project area ranging from hydric to xeric. Data about vegetation, environment, and soil characteristics helped us develop a site plan, vegetation management plan, and revegetation specifications. We also used plant succession field data collected from adjacent clearcuts to determine the desired species composition and spacing for replanting. We planned all the work for this multi-year project by preparing revegetation specifications and requirements in the construction contract. Service crews, temporary employees and volunteers were then trained to carry out plant salvage, seed collection and propagation tasks. Each year, in the early spring before road construction begins, workers salvage most plant materials within the construction zone. They dig 10 to 15.25-cm-thick mats of pioneer grasses/forbs and transplant them directly into high-impact areas like
1990年,美国林务局开始了一项为期四年的项目,以恢复和扩大失落湖的休闲区,该地区自1900年以来一直是露营地。位于喀斯喀特山脉峰顶线以东,海拔957米,项目区每年降雨量为406厘米(160英寸),通常以雪的形式出现。主要植被可描述为属于太平洋银杉(冷杉)植物群落。该项目的目标是建造或重建133个营地和32个日间使用场地,以及超过4.8公里的道路。由于该地区仅在5月至10月期间开放,因此植被恢复被纳入了建设计划。我们的植被恢复目标是:1)尽量减少受建筑干扰的面积,并在这些区域内抢救尽可能多的植物;2)利用在现场或邻近采伐地收集的繁殖体,重新种植所有受干扰地区;3)保护已鉴定植物亚群落的完整性。利用《植物协会和太平洋银杉区管理指南》(Hemstrom et al . 1986)中开发的分类系统,我们在项目区域内确定了四个不同的植物亚群落,从水系到干旱区。关于植被、环境和土壤特征的数据帮助我们制定了场地规划、植被管理计划和植被恢复规范。我们还利用从邻近砍伐地收集的植物演替数据来确定所需的物种组成和补种间距。我们通过在施工合同中准备植被规格和要求来规划这个多年项目的所有工作。然后对服务人员、临时雇员和志愿者进行培训,以执行植物抢救、种子收集和繁殖任务。每年,在道路施工开始前的早春,工人们都会在施工区内打捞大部分植物材料。他们挖出10到15.25厘米厚的先驱草/植物垫,并将它们直接移植到高影响地区,如