Operational forest stream crossings effects on water quality in the Virginia Piedmont

W. Aust, Mathew Carroll, M. Bolding, C. A. Dolloff
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引用次数: 60

Abstract

10–40%. Many ephemeral and intermittent streams in this landscape have unstable banks because they are recovering erosion gullies caused by abusive agricultural practices used in the region in the 1700s and 1800s (Trimble 1974). Common soils of the approaches and stream crossings include the Wehadkee, Chewacla, Wilkes, Appling, Madison, Codorus, Bremo, and Toccoa soil series (USDA Soil Conservation Service 1974). Personnel from three timber procurement organizations and the Virginia Department of Forestry identified potentially suitable stream crossings prior to installation. The first available stream crossings that met the desired criteria was selected, where permission from landowners to make repeated visits could be obtained and where the timing of operations allowed evaluation of the crossing from preinstallation through closure. All stands accessed by the crossings were clearcut harvested and included natural upland hardwood stands and loblolly pine (Pinus taeda L.) plantations. Stream crossings selected were on low-volume forest roads (class 2 permanent roads and class 3 temporary roads) or bladed skid trails (class 4) (Walbridge 1990). The different road classes were included for two reasons, to acquire the desired replications of the crossings in a timely manner and because the different classes represent the overall tract level access system. The roads, skid trails, and crossings included in this study were designed or selected by a company forester or forest engineer and implemented by logging contractors. One difficulty in acquiring the required numbers of stream crossings for the study was caused by the rapid selection and placement of crossings by loggers, which sometimes precluded the required preinstallation measurements. Treatment Description Four stream crossing treatments were evaluated: portable steel skidder bridges (BRIDGE), pole-filled culverts (POLE), reinforced fords (FORD), and standard earth-fill culverts (CULVERT). The initial experimental design sought to install six replications of each crossing structure. However, because of the difficulty in finding more than four sites that were suitable for the FORD, the final design consisted of 6, 6, 4, and 7 replications for the BRIDGE, CULVERT, FORD, and POLE treatments, respectively. Therefore, a total of 23 stream crossings were monitored during the project. The BRIDGE treatment consisted of 9.1–12.2-m (30–40-ft) long steel panels that were 1.2 m (4 ft) wide. Three panels were used for each crossing (Figure 2). POLE crossings used either steel gas line pipes or corrugated steel culverts with pole-sized stems used to fill the stream cross-section (Figure 3). All POLE crossings had stems placed parallel to the pipe as fill; however, some POLE crossings had additional poles or logging mats placed perpendicular to the stream channel to provide a traffic surface. FORD crossings were reinforced with geotextile or mats topped with gravel (Figure 4). Two of four FORD crossings involved simple reinforcements of existing fords on farm roads rather than construction of new fords. CULVERT crossings consisted of either single or double corrugated steel pipes with earth fill (Figure 5). In general, BRIDGE and POLE structures were used for temporary crossings on smaller streams, and CULVERT and FORD structures were used for more permanent roads and larger streams. However, all crossing types were used in at least one instance for both permanent and temporary crossings. These uses match the basic attributes of the crossings: BRIDGE and POLE crossings are better suited for temporary crossings on smaller streams and are often used for skid trails. CULVERT and FORD crossings Figure 1. Virginia physiographic provinces and counties showing the location of the 23 stream crossings evaluated in the Piedmont. Figure 2. BRIDGE treatment using portable steel panels for a temporary haul road stream crossing. 124 SOUTH. J. APPL. FOR. 35(3) 2011 D ow naded rom http/academ ic.p.com /sjaf/article-ct/35/3/123/4774842 by gest on 30 Jauary 2020
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在维吉尼亚皮埃蒙特运营的森林河流过境点对水质的影响
10 - 40%。在这片土地上,许多短暂的间歇溪流的河岸都不稳定,因为它们正在恢复18世纪和19世纪该地区滥用农业实践造成的侵蚀沟渠(Trimble 1974)。途径和河流交叉点的常见土壤包括Wehadkee, Chewacla, Wilkes, Appling, Madison, Codorus, Bremo和Toccoa土壤系列(美国农业部土壤保持服务1974年)。来自三个木材采购组织和弗吉尼亚州林业部的人员在安装之前确定了可能合适的河流过境点。选择了第一个符合预期标准的河流过境点,在那里可以获得土地所有者的许可,可以反复访问,并且作业时间允许对过境点进行评估,从预安装到关闭。所有通过交叉通道的林分均为采伐伐后的林地,包括天然山地硬木林和火炬松人工林。所选择的河流交叉点位于低流量的森林道路(2级永久道路和3级临时道路)或有叶片的滑道(4级)(Walbridge 1990)。包括不同的道路类别有两个原因,一是为了及时获得所需的交叉路口的复制,二是因为不同的类别代表了整个通道级别的访问系统。本研究中包括的道路、滑道和十字路口由公司林务员或森林工程师设计或选择,并由伐木承包商实施。在获得研究所需的河流过境点数量方面的一个困难是由于伐木工人快速选择和放置过境点,这有时妨碍了所需的安装前测量。评估了四种穿越河流的处理方法:便携式钢滑车桥(BRIDGE)、填杆涵洞(POLE)、加固渡口(FORD)和标准填土涵洞(CULVERT)。最初的实验设计试图安装六个交叉结构的复制品。然而,由于很难找到四个以上适合FORD的地点,最终设计分别包括6、6、4和7个BRIDGE、CULVERT、FORD和POLE处理的重复设计。因此,在工程期间,共监察了23个河流过境点。桥梁处理由9.1 - 12.2米(30 - 40英尺)长、1.2米(4英尺)宽的钢板组成。每个交叉点使用三块面板(图2)。极点交叉点使用钢制燃气管线或波纹钢涵洞,带有杆子大小的阀杆,用于填充流的横截面(图3)。所有极点交叉点的阀杆与管道平行,作为填充;然而,一些杆子交叉点有额外的杆子或垂直于河道的伐木垫,以提供一个交通表面。福特十字路口用土工布或铺有砾石的垫子加固(图4)。四个福特十字路口中有两个是对农场道路上现有的渡口进行简单加固,而不是建造新的渡口。涵洞交叉点由单或双波纹钢管和填土组成(图5)。一般来说,BRIDGE和POLE结构用于较小的河流上的临时交叉点,而CULVERT和FORD结构用于更永久的道路和较大的河流。但是,所有过境类型至少在一个实例中用于永久和临时过境。这些用途与交叉路口的基本属性相匹配:桥和杆子交叉路口更适合在较小的溪流上临时交叉,通常用于滑道。图1。维吉尼亚的地理省和县显示了23个河流过境点在皮埃蒙特评估的位置。图2。临时运输道路渡河用可携式钢板处理桥梁。124年南方。j:。对。[35][3] 2011年1月30日,全文:http://academi.ac.p.com /sjaf/ article/35/3/12/4774842
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