ASTM D6146-1997(2007) Standard Guide for Monitoring Aqueous Nutrients in Watersheds《检测分水界水溶氮的标准指南》.pdf

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1、Designation: D 6146 97 (Reapproved 2007)Standard Guide forMonitoring Aqueous Nutrients in Watersheds1This standard is issued under the fixed designation D 6146; the number immediately following the designation indicates the year oforiginal adoption or, in the case of revision, the year of last revis

2、ion. A number in parentheses indicates the year of last reapproval. Asuperscript epsilon (e) indicates an editorial change since the last revision or reapproval.INTRODUCTIONVarious forms of nitrogen and phosphorus are plant nutrients, both naturally occurring andmanmade, that can threaten water reso

3、urces. Nutrients that run off or infiltrate through the soil profilecan result in unfishable and unswimmable streams, lakes, and estuaries, and unsafe surface and groundwater used for drinking. High concentrations of nitrate in drinking water are a threat to young infants,and surface waters can suff

4、er from algal blooms, fish kills, and unpalatable and unsafe water forswimming and drinking. Nutrients are also added to watersheds via chemigation.This guide recommends a process for developing and implementing monitoring projects fornutrients in a watershed. It follows Guide D 5851 with more speci

5、fics applicable to watersheds andnutrients. These guidelines are presented for use in the nationwide strategy for monitoring developedby the Intergovernmental Task Force on Monitoring (ITFM). The nationwide monitoring strategy isan effort to improve the technical aspects of water monitoring to suppo

6、rt sound water qualitydecision-making. It is needed to integrate monitoring activities more effectively and economically toachieve a better return of investments in monitoring projects (1).2Guide D 6145 is offered as a guide for monitoring actual and potential nonpoint and point sourcepollution with

7、in a watershed. The guide is applicable to surface water and ground water resources,recognizing the need for a comprehensive understanding of naturally occurring and manmade impactsto the entire watershed hydrologic system.1. Scope1.1 PurposeThis guide is intended to provide generalguidance on a wat

8、ershed monitoring program directed towardthe plant nutrients nitrogen and phosphorus. The guide offers aseries of general steps without setting forth a specific course ofaction. It gives assistance for developing a monitoring programbut not a program for implementing measures to improve waterquality

9、.1.2 This guide applies to waters found in streams and rivers;lakes, ponds, and reservoirs; estuaries; wetlands; the atmo-sphere; and the vadose and subsurface saturated zones (includ-ing aquifers). This guide does not apply to nutrients found insoils, plants, or animals.1.3 Nutrients as used in thi

10、s guide are intended to includenitrogen and phosphorus in dissolved, gaseous, and particulateforms. Specific species of nitrogen include: nitrate, nitrite,ammonia, organic, total Kjeldahl, and nitrous oxide. Thespecies of phosphorus include total, total dissolved, organic,acid-hydrolyzable, and reac

11、tive phosphorus as described in (2)1.4 SafetyHealth and safety practices developed for aproject may need to consider the following:1.4.1 During the construction of sampling stations:1.4.1.1 Drilling practices during monitoring well installa-tions,1.4.1.2 Overhead and underground utilities during mon

12、itor-ing well drilling,1.4.1.3 Traffic patterns/concerns during sampling stationinstallation,1.4.1.4 Traffic patterns/concerns during surveying samplingstation locations and elevations,1.4.1.5 Drilling through materials highly contaminated withfertilizers, and1.4.1.6 Installing monitoring equipment

13、below the soil sur-face.1.4.2 During the collection of water samples:1.4.2.1 Using acids for sample preservation,1.4.2.2 Sampling during flooding events and ice conditions,1.4.2.3 Traffic on bridges,1.4.2.4 Condition of sampling stations following floodevents,1.4.2.5 Sampling of water or soils, or b

14、oth, highly contami-nated with fertilizers,1This guide is under the jurisdiction of ASTM Committee D19 on Water and isthe direct responsibility of Subcommittee D19.02 on General Specifications,Technical Resources, and Statistical Methods.Current edition approved April 15, 2007. Published April 2007.

15、 Originallyapproved in 1997. Last previous edition approved in 2002 as D 6146 (2002).2The boldface numbers given in parentheses refer to a list of references at theend of this standard.1Copyright ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.

16、1.4.2.6 Conditions of sampling stations resulting from van-dalism,1.4.2.7 Adverse weather conditions, and1.4.2.8 Transporting liquid samples.1.5 This standard does not purport to address all of thesafety concerns, if any, associated with its use. It is theresponsibility of the user of this standard

17、to establish appro-priate safety and health practices and determine the applica-bility of regulatory limitations prior to use.2. Referenced Documents2.1 ASTM Standards:3D 515 Test Methods for Phosphorus in Water4D 653 Terminology Relating to Soil, Rock, and ContainedFluidsD 1129 Terminology Relating

18、 to WaterD 1357 Practice for Planning the Sampling of the AmbientAtmosphereD 1426 Test Methods for Ammonia Nitrogen In WaterD 1739 Test Method for Collection and Measurement ofDustfall (Settleable Particulate Matter)D 3370 Practices for Sampling Water from Closed ConduitsD 3590 Test Methods for Tota

19、l Kjeldahl Nitrogen in WaterD 3856 Guide for Good Laboratory Practices in Laborato-ries Engaged in Sampling and Analysis of WaterD 3858 Test Method for Open-Channel Flow Measurementof Water by Velocity-Area MethodD 3867 Test Methods for Nitrite-Nitrate in WaterD 4410 Terminology for Fluvial Sediment

20、D 4448 Guide for Sampling Ground-Water MonitoringWellsD 4696 Guide for Pore-Liquid Sampling from the VadoseZoneD 4700 Guide for Soil Sampling from the Vadose ZoneD 5092 Practice for Design and Installation of GroundWater Monitoring WellsD 6145 Guide for Monitoring Sediment in WatershedsD 5851 Guide

21、for Planning and Implementing a WaterMonitoring Program3. Terminology3.1 Definitions:3.1.1 For definitions of terms used in this guide, refer toTerminology D 1129 and Guide D 5851.3.2 Definitions of Terms Specific to This Standard:3.2.1 aquifera geologic formation containing water, usu-ally able to

22、yield appreciable water.3.2.2 ground waterthat part of the subsurface water that isthe saturated zone. (D 653, D 18)3.2.3 nonpoint pollutiona condition of water within awater body caused by the presence of undesirable materialsfrom diffuse locations with no particular point of origin.3.2.4 vandose z

23、onethe zone of soil located between thesurface and the water table that is not saturated.3.2.5 watershedall lands enclosed by a continuous hydro-logic surface drainage divide and lying upslope from a speci-fied point on a stream. (D 4410, D 19)4. Significance and Use4.1 The user of this guide is not

24、 assumed to be a trainedtechnical practitioner in the water quality field. The guide is anassembly of the components common to all aspect of water-shed nutrient monitoring and fulfills a need in the developmentof a common framework for a better coordinated and a moreunified approach to nutrient moni

25、toring in watersheds.4.2 LimitationsThis guide does not establish a standardprocedure to follow in all situations and it does not cover thedetail necessary to meet all of the needs of a particularmonitoring objective. Other standards and guides included inthe references describe the detail of the pr

26、ocedures.5. Monitoring Components5.1 A watershed monitoring program of nutrients is com-prised of a series of steps designed to collect nutrient data toachieve a stated objective. The purposes of monitoring may beseveral and include: analyzing trends, studying the fate andtransport of nutrients, def

27、ining critical areas, assessing compli-ance, measuring the effectiveness of management practices,testing for sufficient levels, making wasteload allocations,testing models, defining a water quality problem, and conduct-ing research (3).5.1.1 Monitoring to analyze trends is used to determine howwater

28、 quality is changing over time. In some cases baselinemonitoring is included as the early stage of trend monitoring.5.1.2 Fate and transport monitoring is conducted to deter-mine whether pollutants move and where they may go.5.1.3 Water quality monitoring can be used to locate criticalareas within w

29、atersheds exhibiting greater pollution loadingthan other areas.5.1.4 Nutrient monitoring may also be used to assesscompliance with water quality plans or standards.5.1.5 Nutrient monitoring may assess the effectiveness ofindividual management practices in improving water qualityor, in some cases, ma

30、y be used to evaluate the effect of anentire nutrient management program in a watershed.5.1.6 The testing of nutrient levels in water bodies may beused to see if sufficient amounts are present to support certainaquatic organisms.5.1.7 Monitoring of receiving water bodies may be used todetermine wast

31、eload allocations between point and nonpointsources. Such allocations require a thorough knowledge of theindividual contributions from each source.5.1.8 Nutrient monitoring may be used to fit, calibrate, ortest a model for local conditions.5.1.9 Nutrient monitoring may be used for research ques-tion

32、s such as the accuracy of different types of samplers incollecting a representative sample.5.1.10 Finally, nutrient monitoring may be used to giveadequate definition to a water quality problem or determinewhether a problem exists. Guide for Planning D 5851 providesoverall guidance on water monitorin

33、g.3For referenced ASTM standards, visit the ASTM website, www.astm.org, orcontact ASTM Customer Service at serviceastm.org. For Annual Book of ASTMStandards volume information, refer to the standards Document Summary page onthe ASTM website.4Withdrawn.D 6146 97 (2007)25.1.11 This guide suggests and

34、discusses the following stepsin designing a watershed monitoring program for nutrients.More detail on each step may be found in (3).5.2 Step 1: Water Quality NeedThe first step is to definethe need for nutrient monitoring. The need statement shouldinclude several components: the potential or real wa

35、ter qualityissue requiring attention (for example, eutrophication), thepotential water resource use impairment (for example, recre-ation), the name of the actual water resource (for example,Long Lake), the potential threats or causes (for example,phosphorus), and the potential sources that may cause

36、 aproblem (for example, agriculture) (3). Very often the need isto identify a water quality problem, but in some cases, the needmay be to assess the existing water quality whether a problemexists or not. An example of a need statement might be: “Thelack of recreation in Long Lake is due to excessive

37、 eutrophi-cation caused by excessive phosphorus loading possibly fromagricultural sources.”5.3 Step 2: ObjectivesThe second step in developing anutrient monitoring program is to define the monitoring objec-tives. The objectives of the monitoring study should addressthe water quality need or problem.

38、 An objective statementshould include an infinitive verb, an object word or phrase, andsome limits on the objective such as the surface or groundwater resource or watershed boundaries and variables tomonitor. An example of a monitoring objective might be: “Todetermine the effect of implementing agri

39、cultural managementpractices on phosphorus concentrations in Long Lake.” Whenseveral objectives are used, a hierarchial approach may be usedto determine higher priority objectives. An objective tree canbe used to distinguish among several objectives. To determinehow several objectives can be linked,

40、 the following questioncan be asked: “Does the achievement of objective A contributedirectly to the achievement of objective B?” If it does thenobjective A feeds into objective B and a diagram can be builtshowing all possible objectives and their linkages.5.3.1 To assess whether objectives are being

41、 achieved,objective attributes could be determined. Attributes define thelevel of achievement for each objective. They answer thequestion of how close are we to achieving our goals? Forexample, are we 50 % of the way to achievement? Theseattributes for nutrient monitoring objectives are often binary

42、;that is, either the objective is accomplished or not.5.4 Step 3: Statistical DesignA statistical experimentaldesign should be stated that is consistent with the objectives ofthe monitoring program. Appropriate experimental designscould include: reconnaissance, plot, single watershed, above-and-belo

43、w, two watersheds, paired watershed, multiple water-sheds, and trend stations (3). The design selected will dictatemost other aspects of the monitoring project including thestudy scale, the number of sampling locations, the samplingfrequency, and the station type.5.4.1 Reconnaissance or synoptic des

44、igns may be used as apreliminary survey where no data exist or to assess themagnitude and extent of a problem. This type of samplingcould be used to identify critical areas as well. A critical areais one that is contributing a significant amount of nutrients tothe water body of interest. Randomizati

45、on in sampling loca-tions may be important for reconnaissance monitoring. Recon-naissance monitoring could be used in a “whole aquifer” studywith well placement located randomly or on a grid basis.5.4.2 Plot designs have been commonly used in agriculturalexperiments for 100 years (4). Plots are gene

46、rally small areasthat can be replicated on the land or waterscape. Plots allowreplication and control of certain variables, such as soil type.Plot designs are analyzed using Analysis of Variance (3).5.4.3 The single watershed before-and-after approach hasbeen sometimes used to compare water quality

47、conditionsbefore a watershed treatment to after. Generally, this techniqueis not recommended, since the results are confounded withtime and climate variables, and should be avoided. Forexample, the water quality differences from year-to-year maybe caused by climate differences not the watershed acti

48、vity.5.4.4 The above-and-below design is used after a watershedpractice is in place. Sampling is conducted both upstream anddownstream, or in the case of ground water monitoring,up-gradient and down-gradient from the activity of interest.Although this design is not as susceptible to the effect ofcli

49、mate as the single watershed design, the differences in waterquality between the two stations may be partly due to inherentwatershed differences such as soils or geology. If monitoring isconducted before and after the practice in installed, the designwould follow the paired watershed approach described below.5.4.5 Ground water monitoring using this approach is re-ferred to as up-gradient versus down-gradient monitoring. Thisis probably the most commonly used strategy in ground waterstudies and is appropriate for most designs. Placement of thewells is important because grou