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  • ASTM D6724/D6724M-16
    直接推送地下水監測井安裝指南

    Standard Guide for Installation of Direct Push Groundwater Monitoring Wells


    ASTM D6724/D6724M-16 發布歷史

    ASTM D6724/D6724M-16由美國材料與試驗協會 US-ASTM 發布于 2016-07-01。

    ASTM D6724/D6724M-16在國際標準分類中歸屬于: 13.060.10 天然水資源。

    ASTM D6724/D6724M-16 直接推送地下水監測井安裝指南的最新版本是哪一版?

    最新版本是 ASTM D6724/D6724M-16(2024)e1

    ASTM D6724/D6724M-16 發布之時,引用了標準

    • ASTM D3740 工程設計及建筑中使用的土壤和巖石的試驗和或檢查中使用試劑評定的規程
    • ASTM D4448 地下水監測井取樣的標準指南
    • ASTM D4750 測定鉆井或監測井(觀察井)中地下水位的試驗方法
    • ASTM D5088 非放射性廢物場用現場設備凈化的標準實施規程
    • ASTM D5092 蓄水層中的地下水監測井的設計和安裝的標準實施規程
    • ASTM D5254 識別地下水位用數據元最小集合的標準規程
    • ASTM D5299 測定環境活性物質用地下水井、包氣帶監測裝置、鉆孔及其他設備退役的標準指南
    • ASTM D5434 土壤和巖石地下爆炸現場記錄的標準導則
    • ASTM D5474 地下水調查數據元選擇標準指南
    • ASTM D5521 粒狀含水層地下水監測井開發標準指南(2003 年撤回)
    • ASTM D5730 重點在土壤,巖石,滲流區和地表水的環境要求的標準指南
    • ASTM D5978 地下水監測井維護和恢復標準指南
    • ASTM D6001 地質環境調查用直接推進水取樣的標準指南
    • ASTM D6026 在土工學數據中使用明顯數字的標準實施規程
    • ASTM D6067 環境定位特性用電子錐形透度計使用的標準指南
    • ASTM D6282 環境位點特性分析用直推土壤采樣的標準指南
    • ASTM D6286 環境位點特性分析用鉆削方法選擇的標準指南
    • ASTM D6452 地下水質檢測井清潔方法的標準指南
    • ASTM D653 采用流動空氣測量未飽和多孔材料滲透性的標準試驗方法
    • ASTM D6564 地下水樣品現場過濾的標準指南*2024-09-02 更新
    • ASTM D6634 地下水監測井用凈化和取樣選擇的標準指南*2024-09-02 更新
    • ASTM D6725 未固結含水土層里預制的濾網式監測井的直推式安裝的標準實施規程*2024-09-02 更新
    • ASTM D6771 地下水監測用低流量吹掃和取樣的標準實施規程*2021-11-01 更新
    • ASTM D6914 地下監視設備的場地特征和安裝的聲鉆法標準規程*2024-09-02 更新
    • ASTM D7242 用直推式地下水取樣器測定蓄水層液壓特性的現場氣動排料孔(水頭瞬息變化)試驗的標準實施規范*2024-09-02 更新
    • ASTM D7352 用直接推壓法在松散地層中使用膜界面探針(MIP)進行揮發性污染物測井的標準實施規程*2018-07-15 更新
    • ASTM D7929 用于抽取地下水監測井被動技術的標準指南*2020-02-15 更新

    * 在 ASTM D6724/D6724M-16 發布之后有更新,請注意新發布標準的變化。

    ASTM D6724/D6724M-16的歷代版本如下:

     

    5.1 The direct push ground method is a rapid and economical procedure for installing groundwater monitoring wells to obtain representative groundwater samples and location-specific hydrogeologic measurements. Direct push installations may offer an advantage over conventional rotary drilled monitoring wells (Practice D5092) for groundwater explorations in unconsolidated formations because they reduce disturbance to the formation, and eliminate or minimize drill cuttings. At facilities where contaminated soils are present, this can reduce hazard exposure for operators, local personnel, and the environment, and can reduce investigative derived wastes. Additionally, smaller equipment can be used for installation, providing better access to constricted locations.

    5.2 Direct push monitoring wells are typically smaller in diameter than drilled wells, thereby reducing purge water volumes, sampling time, and investigative derived wastes. Practice D5092 monitoring wells are used when larger diameters and/or sample volumes are required, or at depths or in geologic formations to where it is difficult to install direct push wells. Direct push monitoring wells should be viable for monitoring for many years.

    5.3 Prior to construction and installation of a direct push well or any other type of groundwater well the reader should consult appropriate local agencies regarding regulatory requirements for well construction. A regulatory variance may be required for installation of direct push monitoring wells.

    5.4 To date, published comparison studies between drilled monitoring wells and direct push monitoring wells have shown comparability (1-10)4. However, selection of direct push monitoring wells over conventional rotary drilled wells should be based on several criteria, such as site accessibility and penetrability, stratigraphic structure, depth to groundwater, and aquifer transmissivity.

    5.5 Typical penetration depths for installation of groundwater monitoring wells with direct push equipment depend on many variables. Some of the variables are the size and type of the driving system, diameter of the drive rods and monitoring well, and the resistance of the earth materials being penetrated. Some direct push systems are capable of installing groundwater monitoring wells to depths in excess of 100 ft [30 m], and larger direct push equipment can reach depths of several hundred feet. However, installation depths of 10 to 50 ft [5 to 15 m] are most common. Direct push methods cannot be used to install monitoring wells in consolidated bedrock (for example, granite, limestone, gneiss), but are intended for installation in unconsolidated materials such as clays, silts, sands, and some gravels. Additionally, deposits containing significant cobbles and boulders (for example, some glacial deposits), or strongly cemented materials (for example, caliche) are likel......


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