{"title":"1999-2002年缅因州的干旱状况:一个历史的视角","authors":"P. Lombard","doi":"10.3133/WRI034310","DOIUrl":null,"url":null,"abstract":"Hydrologic drought can be defined as reduced streamflow, declining ground-water levels, and (or) reductions in lake or reservoir levels. Monthly precipitation totals, annual 7-day low-flow surface-water recurrence intervals, and month-end ground-water levels from drought years 1999-2002 show that 19992002 was the driest period of hydrologic drought in more than 50 years of record in Maine. Record lows were set in all three data sets at select locations in central Maine in April 1999, and in September 2001 and 2002. Although streamflows recovered to normal levels during 2000, ground-water levels in central Maine indicate that the drought carried over through 2000 into 2001 and 2002 in some locations. In 2001, annual 7-day low flows with greater than 100-year recurrence intervals were recorded in central Maine and low flows with up to 75-year recurrence intervals were recorded in coastal areas. In 2002, annual 7-day low flows with greater than 100-year recurrence intervals were recorded at 4 of 14 stations analyzed statewide, placing it as the driest single year of hydrologic drought on record. Month-end groundwater levels at one location in central Maine indicate that the recent hydrologic drought years were the most severe in more than 50 years in that region. The period from 1947 to 1950 may have been the only comparable period of drought to the 1999-2002 period, in Maine. The 1960s drought, although extreme in the far northern and far southern regions of the State, was most exceptional for its duration from 1963 to 1969. INTRODUCTION Drought is among the most complex and least understood of all natural hazards, affecting more people than any other natural hazard (American Meteorological Society, 1997). Although drought typically is not considered a problem in the humid northeastern United States, it is a normal, recurring feature in all climatic regimes. Drought is a temporary aberration, relative to some long-term (tens of years) average condition, as opposed to aridity, which is a permanent feature of some regional climates (American Meteorological Society, 1997). Many questions still remain concerning the physical mechanisms responsible for the onset, persistence, and spatial extent of regional hydrologic drought in the northeast because of hydrologic variability and the inherent complexity of hydrologic systems (Bradbury and others, 2002). Dry conditions were present in Maine from 1999 to 2002, with a severe drought in 2001-2002. Most U.S.Geological Survey (USGS) monitoring wells, and many streamflow-gaging stations, set record lows during this period. An estimated 7 percent, or approximately 17,000 private wells in Maine went dry in the 9 months prior to April 2002 (Maine Emergency Management Agency, 2002). Wells in central Maine were the most likely to have low water levels. Thirtyfive public water supplies, including eight large community systems, were affected severely (Andrews Tolman, Maine Drinking Water Program, written communication, 2003). Most major surface-water reservoirs released water at levels below their regulatory minimum flows, instream flows for aquatic life were reduced, and critical summer irrigation was limited. Farmers in Maine lost more than 32 million dollars in crops in 2001 and 2002, with some wild blueberry growers recording crop losses of 80 to 100 percent according to a Maine Department of Agriculture water-use survey to which 28 percent of Maine farmers responded (Maine Agricultural Water Management Advisory Committee, 2003). The effects of past droughts nationwide have been exacerbated by the absence of preparedness plans (American Meteorological Society, 1997). An integral part of any preparedness plan would include meteorologic and hydrologic thresholds based on historical Abstract 1 droughts in the region. During 1999-2002, waterresource professionals, farmers, business owners, and others who were concerned with instream flows, storage, or ground-water levels lacked the quantitative historical information necessary to compare the severity of the 1999 to 2002 drought to historical droughts, and to assess the potential of drought to stress water resources. Because droughts will occur in Maine in the future, water-resource professionals will benefit from documentation and analysis of the hydrologic conditions experienced from 1999 to 2002 in Maine. In particular, emergency management workers and public-water suppliers in Maine will benefit from this information by better understanding the complexity of how droughts move through the hydrologic system, and thus, be better able to anticipate drought effects. Purpose and Scope The purpose of this report is to document the relative regional and historical severity of the dry hydrologic conditions experienced from 1999 to 2002, and to provide information regarding the occurrence and persistence of droughts in Maine. This report includes a comparison of 1999-2002 daily mean streamflows, month-end ground-water levels, and total monthly precipitation values to historical statistics at select stations. The interaction among precipitation, surface water, and ground water, the annual 7-day surface-water low-flow recurrence intervals for this drought period and for historical droughts, and a comparison of month-end ground-water levels to ground-water statistics for historical droughts also are examined. Drought Definition Droughts can be measured or defined on the basis of a wide variety of parameters including precipitation deficits, streamflows, ground-water levels, soil moisture, and economic impacts. The relation among the intensity, duration, and spatial and temporal extent of these parameters defines many different types of events, all of which may be considered droughts. For example, a growing season with no rain in the northern region of the State would be characterized differently than a statewide, multi-year period with below-average precipitation, but both could be considered droughts. Although drought can be defined strictly as a percentage of normal precipitation, it is more often defined as a period of moisture deficit sufficient to have some adverse effect on the social or economic activity of a region (Changnon, 1980; Paulson and others, 1991). The integration of multiple definitions into a combined measure of drought has been problematic in the past for natural resource managers. The many definitions of drought make it difficult to declare the beginning or end of a drought or assess its severity during a drought period. The American Meteorological Society groups drought into four types including climatologic drought, agricultural drought, hydrologic drought, and socioeconomic drought (American Meteorological Society, 1997). Climatologic drought often is defined by a threshold precipitation deficit or a ratio of actual precipitation to normal precipitation. Agricultural drought links climatologic drought to agricultural effects and is largely the result of a deficit of soil moisture. Hydrologic drought is defined as reduced streamflow, declining ground-water levels, and (or) reductions in lake or storage levels. Socioeconomic drought associates the supply and demand of some economic good with the elements of climatologic, agricultural, and (or) hydrologic drought (American Meteorological Society, 1997). These types of drought usually take place simultaneously; however, hydrologic droughts typically are out of phase with or lag climatologic and agricultural droughts. Meteorologic elements, such as temperature, wind, and relative humidity, can aggravate the severity and the effects of drought (American Meteorological Society, 1997). Although various aspects of all four drought types defined here occurred in Maine from 1999 to 2002, this report primarily documents the characteristics of the hydrologic drought and how the climatologic drought contributed to it. Previous Studies There is very little documentation of historical droughts in Maine. In 1991, the USGS defined multiyear historical droughts in each state of the United States, and calculated their recurrence intervals in a National Water Summary on floods and droughts (Paulson and others, 1991). Drought periods identified for the Maine Water Summary are listed in table 1 (Maloney and Bartlett, 1991): 2 Drought Conditions in Maine, 1999-2002: A Historical Perspective Table 1. Low-flow recurrence intervals for historical droughts in Maine from 1938 to 1988, as identified by Maloney and Bartlett in the National Water Summary, 1991 [Low-flow recurrence interval, the average interval of time within which streamflow will be less than a particular value; >, greater than] The recurrence intervals for the droughts in table 1 were calculated on the basis of the cumulative departure from mean monthly streamflows. This method is described in the introduction to State summaries of floods and droughts in the National Water Summary (Jordan and Jennings, 1991). The intensity of the drought was taken into account, but the duration was not; droughts that varied in duration from 1 year to 6 years were ranked on the same scale. This method may be appropriate for identifying multi-year periods of drought, or assigning recurrence intervals to total water deficits in systems that depend on reservoirs such as in the western United States, but it is not appropriate for eastern States except in the most approximate terms. This is because drought in the eastern United States may depend on the timing of precipitation as much as on the total amount of precipitation. Resource managers in the northeastern United States often use national indices to assess regional conditions despite that these indices may be more appropriate for nationwide water-status monitoring (Skaggs, 1975). Often, the national indices fail to give those affected by the drought or those who make policy a local basis for evaluation and action (Russell, and others, 1970). Even different user groups within a region may experien","PeriodicalId":23603,"journal":{"name":"Water-Resources Investigations Report","volume":"1 1","pages":""},"PeriodicalIF":0.0000,"publicationDate":"2004-01-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"11","resultStr":"{\"title\":\"Drought Conditions in Maine, 1999-2002: A Historical Perspective\",\"authors\":\"P. Lombard\",\"doi\":\"10.3133/WRI034310\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"Hydrologic drought can be defined as reduced streamflow, declining ground-water levels, and (or) reductions in lake or reservoir levels. Monthly precipitation totals, annual 7-day low-flow surface-water recurrence intervals, and month-end ground-water levels from drought years 1999-2002 show that 19992002 was the driest period of hydrologic drought in more than 50 years of record in Maine. Record lows were set in all three data sets at select locations in central Maine in April 1999, and in September 2001 and 2002. Although streamflows recovered to normal levels during 2000, ground-water levels in central Maine indicate that the drought carried over through 2000 into 2001 and 2002 in some locations. In 2001, annual 7-day low flows with greater than 100-year recurrence intervals were recorded in central Maine and low flows with up to 75-year recurrence intervals were recorded in coastal areas. In 2002, annual 7-day low flows with greater than 100-year recurrence intervals were recorded at 4 of 14 stations analyzed statewide, placing it as the driest single year of hydrologic drought on record. Month-end groundwater levels at one location in central Maine indicate that the recent hydrologic drought years were the most severe in more than 50 years in that region. The period from 1947 to 1950 may have been the only comparable period of drought to the 1999-2002 period, in Maine. The 1960s drought, although extreme in the far northern and far southern regions of the State, was most exceptional for its duration from 1963 to 1969. INTRODUCTION Drought is among the most complex and least understood of all natural hazards, affecting more people than any other natural hazard (American Meteorological Society, 1997). Although drought typically is not considered a problem in the humid northeastern United States, it is a normal, recurring feature in all climatic regimes. Drought is a temporary aberration, relative to some long-term (tens of years) average condition, as opposed to aridity, which is a permanent feature of some regional climates (American Meteorological Society, 1997). Many questions still remain concerning the physical mechanisms responsible for the onset, persistence, and spatial extent of regional hydrologic drought in the northeast because of hydrologic variability and the inherent complexity of hydrologic systems (Bradbury and others, 2002). Dry conditions were present in Maine from 1999 to 2002, with a severe drought in 2001-2002. Most U.S.Geological Survey (USGS) monitoring wells, and many streamflow-gaging stations, set record lows during this period. An estimated 7 percent, or approximately 17,000 private wells in Maine went dry in the 9 months prior to April 2002 (Maine Emergency Management Agency, 2002). Wells in central Maine were the most likely to have low water levels. Thirtyfive public water supplies, including eight large community systems, were affected severely (Andrews Tolman, Maine Drinking Water Program, written communication, 2003). Most major surface-water reservoirs released water at levels below their regulatory minimum flows, instream flows for aquatic life were reduced, and critical summer irrigation was limited. Farmers in Maine lost more than 32 million dollars in crops in 2001 and 2002, with some wild blueberry growers recording crop losses of 80 to 100 percent according to a Maine Department of Agriculture water-use survey to which 28 percent of Maine farmers responded (Maine Agricultural Water Management Advisory Committee, 2003). The effects of past droughts nationwide have been exacerbated by the absence of preparedness plans (American Meteorological Society, 1997). An integral part of any preparedness plan would include meteorologic and hydrologic thresholds based on historical Abstract 1 droughts in the region. During 1999-2002, waterresource professionals, farmers, business owners, and others who were concerned with instream flows, storage, or ground-water levels lacked the quantitative historical information necessary to compare the severity of the 1999 to 2002 drought to historical droughts, and to assess the potential of drought to stress water resources. Because droughts will occur in Maine in the future, water-resource professionals will benefit from documentation and analysis of the hydrologic conditions experienced from 1999 to 2002 in Maine. In particular, emergency management workers and public-water suppliers in Maine will benefit from this information by better understanding the complexity of how droughts move through the hydrologic system, and thus, be better able to anticipate drought effects. Purpose and Scope The purpose of this report is to document the relative regional and historical severity of the dry hydrologic conditions experienced from 1999 to 2002, and to provide information regarding the occurrence and persistence of droughts in Maine. This report includes a comparison of 1999-2002 daily mean streamflows, month-end ground-water levels, and total monthly precipitation values to historical statistics at select stations. The interaction among precipitation, surface water, and ground water, the annual 7-day surface-water low-flow recurrence intervals for this drought period and for historical droughts, and a comparison of month-end ground-water levels to ground-water statistics for historical droughts also are examined. Drought Definition Droughts can be measured or defined on the basis of a wide variety of parameters including precipitation deficits, streamflows, ground-water levels, soil moisture, and economic impacts. The relation among the intensity, duration, and spatial and temporal extent of these parameters defines many different types of events, all of which may be considered droughts. For example, a growing season with no rain in the northern region of the State would be characterized differently than a statewide, multi-year period with below-average precipitation, but both could be considered droughts. Although drought can be defined strictly as a percentage of normal precipitation, it is more often defined as a period of moisture deficit sufficient to have some adverse effect on the social or economic activity of a region (Changnon, 1980; Paulson and others, 1991). The integration of multiple definitions into a combined measure of drought has been problematic in the past for natural resource managers. The many definitions of drought make it difficult to declare the beginning or end of a drought or assess its severity during a drought period. The American Meteorological Society groups drought into four types including climatologic drought, agricultural drought, hydrologic drought, and socioeconomic drought (American Meteorological Society, 1997). Climatologic drought often is defined by a threshold precipitation deficit or a ratio of actual precipitation to normal precipitation. Agricultural drought links climatologic drought to agricultural effects and is largely the result of a deficit of soil moisture. Hydrologic drought is defined as reduced streamflow, declining ground-water levels, and (or) reductions in lake or storage levels. Socioeconomic drought associates the supply and demand of some economic good with the elements of climatologic, agricultural, and (or) hydrologic drought (American Meteorological Society, 1997). These types of drought usually take place simultaneously; however, hydrologic droughts typically are out of phase with or lag climatologic and agricultural droughts. 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Low-flow recurrence intervals for historical droughts in Maine from 1938 to 1988, as identified by Maloney and Bartlett in the National Water Summary, 1991 [Low-flow recurrence interval, the average interval of time within which streamflow will be less than a particular value; >, greater than] The recurrence intervals for the droughts in table 1 were calculated on the basis of the cumulative departure from mean monthly streamflows. This method is described in the introduction to State summaries of floods and droughts in the National Water Summary (Jordan and Jennings, 1991). The intensity of the drought was taken into account, but the duration was not; droughts that varied in duration from 1 year to 6 years were ranked on the same scale. 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引用次数: 11
摘要
水文干旱可以定义为河流流量减少、地下水位下降和(或)湖泊或水库水位下降。1999-2002年干旱年的月降水总量、年7天低流量地表水重现间隔和月末地下水位表明,1999-2002年是缅因州50多年来水文干旱最干旱的时期。1999年4月、2001年9月和2002年9月,缅因州中部选定地点的所有三个数据集都创下了历史新低。虽然河流流量在2000年恢复到正常水平,但缅因州中部的地下水位表明,在一些地方,干旱持续了2000年至2001年和2002年。2001年,缅因州中部记录到的年7天低流量大于100年的重现间隔,沿海地区记录到的年低流量高达75年的重现间隔。2002年,在全州分析的14个站点中,有4个站点记录了超过100年重复周期的7天低流量,使其成为有记录以来最干旱的水文干旱年。缅因州中部一个地方月末的地下水位表明,最近的水文干旱年份是该地区50多年来最严重的。1947年至1950年可能是缅因州唯一可与1999年至2002年相比的干旱时期。1960年代的干旱虽然在该国最北部和最南部地区极为严重,但在1963年至1969年期间却是最为罕见的。干旱是所有自然灾害中最复杂和最不为人所知的灾害之一,影响的人数比任何其他自然灾害都多(美国气象学会,1997年)。尽管干旱在潮湿的美国东北部通常不被认为是一个问题,但它在所有气候制度中都是一个正常的、反复出现的特征。相对于一些长期(几十年)的平均状况,干旱是一种暂时的失常,而干旱是一些区域气候的永久特征(美国气象学会,1997年)。由于水文变异性和水文系统固有的复杂性,东北地区区域性水文干旱的发生、持续和空间范围的物理机制仍然存在许多问题(Bradbury等,2002)。1999年至2002年,缅因州一直处于干旱状态,2001年至2002年发生了严重干旱。大多数美国地质调查局(USGS)的监测井和许多流量测量站在此期间创下了历史新低。在2002年4月之前的9个月里,缅因州约有7%的私人水井干涸(缅因州紧急事务管理局,2002年)。缅因州中部的水井最有可能出现低水位。35个公共供水系统,包括8个大型社区供水系统,受到严重影响(Andrews Tolman, Maine Drinking water Program, written communication, 2003)。大多数主要地表水水库的放水量低于其调节最小流量,水生生物的溪流流量减少,关键的夏季灌溉受到限制。缅因州农业部的一项用水调查显示,2001年和2002年,缅因州农民的农作物损失超过3200万美元,其中一些野生蓝莓种植者的作物损失高达80%至100%,28%的缅因州农民对此作出了回应(缅因州农业用水管理咨询委员会,2003年)。由于缺乏防备计划,过去全国范围内干旱的影响已经加剧(美国气象学会,1997年)。任何准备计划的一个组成部分将包括基于该地区历史干旱的气象和水文阈值。在1999-2002年期间,水资源专业人士、农民、企业主和其他关注河流流量、储水量或地下水位的人缺乏必要的定量历史信息,无法将1999-2002年干旱的严重程度与历史干旱进行比较,也无法评估干旱对水资源造成压力的潜力。由于未来缅因州将发生干旱,水资源专家将受益于1999年至2002年缅因州水文条件的记录和分析。特别是,缅因州的应急管理人员和公共供水供应商将从这些信息中受益,因为他们可以更好地了解干旱如何在水文系统中移动的复杂性,从而更好地预测干旱的影响。本报告的目的是记录1999年至2002年干旱水文条件的相对区域和历史严重程度,并提供有关缅因州干旱发生和持续的信息。 本报告将1999-2002年的日平均流量、月末地下水位和月总降水量与选定站点的历史统计数据进行了比较。本文还研究了降水、地表水和地下水之间的相互作用,这次干旱期和历史干旱的每年7天地表水低流量重复周期,以及历史干旱的月末地下水水位与地下水统计数据的比较。干旱可以根据多种参数进行测量或定义,包括降水不足、河流流量、地下水位、土壤湿度和经济影响。这些参数的强度、持续时间和时空范围之间的关系定义了许多不同类型的事件,所有这些事件都可以被认为是干旱。例如,该州北部地区没有降雨的生长季节与全州范围内降雨量低于平均水平的多年期的特征不同,但两者都可以被认为是干旱。尽管干旱可以严格地定义为正常降水的百分比,但它更经常被定义为一段时间的水分不足,足以对一个地区的社会或经济活动产生一些不利影响(Changnon, 1980;保尔森等人,1991)。在过去,对自然资源管理人员来说,将多种定义整合到干旱的综合测量中是有问题的。干旱的许多定义使得很难宣布干旱的开始或结束,或在干旱期间评估其严重程度。美国气象学会将干旱分为四种类型,包括气候干旱、农业干旱、水文干旱和社会经济干旱(American Meteorological Society, 1997)。气候干旱通常由降水亏缺阈值或实际降水与正常降水之比来定义。农业干旱将气候干旱与农业效应联系在一起,主要是土壤水分缺乏的结果。水文干旱的定义是河流流量减少、地下水位下降和(或)湖泊或水库水位减少。社会经济干旱将一些经济产品的供给和需求与气候、农业和(或)水文干旱的要素联系在一起(美国气象学会,1997)。这些类型的干旱通常同时发生;然而,水文干旱通常与气候干旱和农业干旱不同步或滞后。气象因素,如温度、风和相对湿度,可以加剧干旱的严重程度和影响(美国气象学会,1997)。尽管这里定义的四种干旱类型的各个方面都发生在1999年至2002年的缅因州,但本报告主要记录了水文干旱的特征以及气候干旱是如何促成它的。以前的研究很少有关于缅因州历史干旱的记录。1991年,美国地质勘探局在美国各州定义了多年的历史干旱,并在一份关于洪水和干旱的国家水资源摘要中计算了它们的复发间隔(Paulson等人,1991)。《缅因州水资源概况》确定的干旱期列于表1 (Maloney和Bartlett, 1991): 2 1999-2002年缅因州的干旱状况:历史视角。由Maloney和Bartlett在1991年的《国家水资源概要》中确定的1938 - 1988年缅因州历史干旱的低流量复发间隔[低流量复发间隔,流量小于特定值的平均时间间隔;表1中干旱的复发间隔是根据与月平均流量的累积偏差计算的。这种方法在《国家水资源概要》(Jordan and Jennings, 1991)中对各州洪水和干旱摘要的介绍部分进行了描述。干旱的强度被考虑在内,但持续时间没有考虑在内;持续时间从1年到6年不等的干旱在相同的尺度上排名。这种方法可能适用于确定多年的干旱期,或在美国西部等依赖水库的系统中为总缺水分配复发间隔,但除了最近似的条件外,它不适用于东部各州。这是因为美国东部的干旱既取决于降水总量,也取决于降水时间。美国东北部的资源管理人员经常使用国家指数来评估区域条件,尽管这些指数可能更适合全国范围的水状况监测(Skaggs, 1975)。 通常,国家指数不能给那些受干旱影响的人或那些制定政策的人提供地方评价和行动的基础(Russell等人,1970年)。甚至一个地区内的不同用户组也可能经历
Drought Conditions in Maine, 1999-2002: A Historical Perspective
Hydrologic drought can be defined as reduced streamflow, declining ground-water levels, and (or) reductions in lake or reservoir levels. Monthly precipitation totals, annual 7-day low-flow surface-water recurrence intervals, and month-end ground-water levels from drought years 1999-2002 show that 19992002 was the driest period of hydrologic drought in more than 50 years of record in Maine. Record lows were set in all three data sets at select locations in central Maine in April 1999, and in September 2001 and 2002. Although streamflows recovered to normal levels during 2000, ground-water levels in central Maine indicate that the drought carried over through 2000 into 2001 and 2002 in some locations. In 2001, annual 7-day low flows with greater than 100-year recurrence intervals were recorded in central Maine and low flows with up to 75-year recurrence intervals were recorded in coastal areas. In 2002, annual 7-day low flows with greater than 100-year recurrence intervals were recorded at 4 of 14 stations analyzed statewide, placing it as the driest single year of hydrologic drought on record. Month-end groundwater levels at one location in central Maine indicate that the recent hydrologic drought years were the most severe in more than 50 years in that region. The period from 1947 to 1950 may have been the only comparable period of drought to the 1999-2002 period, in Maine. The 1960s drought, although extreme in the far northern and far southern regions of the State, was most exceptional for its duration from 1963 to 1969. INTRODUCTION Drought is among the most complex and least understood of all natural hazards, affecting more people than any other natural hazard (American Meteorological Society, 1997). Although drought typically is not considered a problem in the humid northeastern United States, it is a normal, recurring feature in all climatic regimes. Drought is a temporary aberration, relative to some long-term (tens of years) average condition, as opposed to aridity, which is a permanent feature of some regional climates (American Meteorological Society, 1997). Many questions still remain concerning the physical mechanisms responsible for the onset, persistence, and spatial extent of regional hydrologic drought in the northeast because of hydrologic variability and the inherent complexity of hydrologic systems (Bradbury and others, 2002). Dry conditions were present in Maine from 1999 to 2002, with a severe drought in 2001-2002. Most U.S.Geological Survey (USGS) monitoring wells, and many streamflow-gaging stations, set record lows during this period. An estimated 7 percent, or approximately 17,000 private wells in Maine went dry in the 9 months prior to April 2002 (Maine Emergency Management Agency, 2002). Wells in central Maine were the most likely to have low water levels. Thirtyfive public water supplies, including eight large community systems, were affected severely (Andrews Tolman, Maine Drinking Water Program, written communication, 2003). Most major surface-water reservoirs released water at levels below their regulatory minimum flows, instream flows for aquatic life were reduced, and critical summer irrigation was limited. Farmers in Maine lost more than 32 million dollars in crops in 2001 and 2002, with some wild blueberry growers recording crop losses of 80 to 100 percent according to a Maine Department of Agriculture water-use survey to which 28 percent of Maine farmers responded (Maine Agricultural Water Management Advisory Committee, 2003). The effects of past droughts nationwide have been exacerbated by the absence of preparedness plans (American Meteorological Society, 1997). An integral part of any preparedness plan would include meteorologic and hydrologic thresholds based on historical Abstract 1 droughts in the region. During 1999-2002, waterresource professionals, farmers, business owners, and others who were concerned with instream flows, storage, or ground-water levels lacked the quantitative historical information necessary to compare the severity of the 1999 to 2002 drought to historical droughts, and to assess the potential of drought to stress water resources. Because droughts will occur in Maine in the future, water-resource professionals will benefit from documentation and analysis of the hydrologic conditions experienced from 1999 to 2002 in Maine. In particular, emergency management workers and public-water suppliers in Maine will benefit from this information by better understanding the complexity of how droughts move through the hydrologic system, and thus, be better able to anticipate drought effects. Purpose and Scope The purpose of this report is to document the relative regional and historical severity of the dry hydrologic conditions experienced from 1999 to 2002, and to provide information regarding the occurrence and persistence of droughts in Maine. This report includes a comparison of 1999-2002 daily mean streamflows, month-end ground-water levels, and total monthly precipitation values to historical statistics at select stations. The interaction among precipitation, surface water, and ground water, the annual 7-day surface-water low-flow recurrence intervals for this drought period and for historical droughts, and a comparison of month-end ground-water levels to ground-water statistics for historical droughts also are examined. Drought Definition Droughts can be measured or defined on the basis of a wide variety of parameters including precipitation deficits, streamflows, ground-water levels, soil moisture, and economic impacts. The relation among the intensity, duration, and spatial and temporal extent of these parameters defines many different types of events, all of which may be considered droughts. For example, a growing season with no rain in the northern region of the State would be characterized differently than a statewide, multi-year period with below-average precipitation, but both could be considered droughts. Although drought can be defined strictly as a percentage of normal precipitation, it is more often defined as a period of moisture deficit sufficient to have some adverse effect on the social or economic activity of a region (Changnon, 1980; Paulson and others, 1991). The integration of multiple definitions into a combined measure of drought has been problematic in the past for natural resource managers. The many definitions of drought make it difficult to declare the beginning or end of a drought or assess its severity during a drought period. The American Meteorological Society groups drought into four types including climatologic drought, agricultural drought, hydrologic drought, and socioeconomic drought (American Meteorological Society, 1997). Climatologic drought often is defined by a threshold precipitation deficit or a ratio of actual precipitation to normal precipitation. Agricultural drought links climatologic drought to agricultural effects and is largely the result of a deficit of soil moisture. Hydrologic drought is defined as reduced streamflow, declining ground-water levels, and (or) reductions in lake or storage levels. Socioeconomic drought associates the supply and demand of some economic good with the elements of climatologic, agricultural, and (or) hydrologic drought (American Meteorological Society, 1997). These types of drought usually take place simultaneously; however, hydrologic droughts typically are out of phase with or lag climatologic and agricultural droughts. Meteorologic elements, such as temperature, wind, and relative humidity, can aggravate the severity and the effects of drought (American Meteorological Society, 1997). Although various aspects of all four drought types defined here occurred in Maine from 1999 to 2002, this report primarily documents the characteristics of the hydrologic drought and how the climatologic drought contributed to it. Previous Studies There is very little documentation of historical droughts in Maine. In 1991, the USGS defined multiyear historical droughts in each state of the United States, and calculated their recurrence intervals in a National Water Summary on floods and droughts (Paulson and others, 1991). Drought periods identified for the Maine Water Summary are listed in table 1 (Maloney and Bartlett, 1991): 2 Drought Conditions in Maine, 1999-2002: A Historical Perspective Table 1. Low-flow recurrence intervals for historical droughts in Maine from 1938 to 1988, as identified by Maloney and Bartlett in the National Water Summary, 1991 [Low-flow recurrence interval, the average interval of time within which streamflow will be less than a particular value; >, greater than] The recurrence intervals for the droughts in table 1 were calculated on the basis of the cumulative departure from mean monthly streamflows. This method is described in the introduction to State summaries of floods and droughts in the National Water Summary (Jordan and Jennings, 1991). The intensity of the drought was taken into account, but the duration was not; droughts that varied in duration from 1 year to 6 years were ranked on the same scale. This method may be appropriate for identifying multi-year periods of drought, or assigning recurrence intervals to total water deficits in systems that depend on reservoirs such as in the western United States, but it is not appropriate for eastern States except in the most approximate terms. This is because drought in the eastern United States may depend on the timing of precipitation as much as on the total amount of precipitation. Resource managers in the northeastern United States often use national indices to assess regional conditions despite that these indices may be more appropriate for nationwide water-status monitoring (Skaggs, 1975). Often, the national indices fail to give those affected by the drought or those who make policy a local basis for evaluation and action (Russell, and others, 1970). Even different user groups within a region may experien