Home :: Leadership :: Objectives :: Accomplishments :: Facts :: Join ::  Endorsements  :: Contact

Watershed Maps ::  Current Flow  & Temps ::  Archives :: Flood Plain Tributary Restoration Plan

HABITAT BANKS, THERMAL BANKS, AND TEMPERATURE TARGETS

 

THE PROBLEM WITH HABITAT BANKS, THERMAL BANKS, TEMPERATURE TARGETS AND FLOW TARGETS

 Any fisheries management plan for the Delaware River tail water trout fishery that is based on habitat banks, thermal banks, temperature targets and flow targets depends on the accuracy and timeliness of a bewildering number of assumptions, predictions and monitoring ability.  In order to be effective, such a plan needs to accurately monitor, on a continuing basis, water and air temperature and flow conditions at a number of locations AND be able to predict, far enough in advance, the effect that a certain amount of water at a particular temperature and flow will have on a living resource tens of miles downstream, tens of hours later.  Even more problematic is the ability to estimate, a year or more in advance, how much water should be allocated to these banks.

 EFFECT OF NON-MONITORED TRIBUTARIES AND WEATHER

 The temperature and flow of tributaries and springs within the three main tributaries have a profound but unmeasured effect on the temperature and flow in the designated trout management sections.  The Delaware River system spans hundreds of miles.  Local weather conditions have important, unpredictable and often un-recorded effects on the waters under consideration. 

 MONITORING AND LOCATION OF GAGES

 Water temperatures and flow change rapidly as a function of the amount of water being released from the reservoirs and local weather conditions.  On any particular summer day, one tributary may be receiving mostly cold water from releases whereas another tributary may consist almost entirely of flow from unmonitored tributaries to that stream.  In order for a system based on temperature and flow targets to be effective, the location of key temperature and flow gages must not only be calibrated frequently for accuracy, they must be located in places that adequately reflect conditions that are of significance to the resources to be protected.

 PREDICTION AND LAG TIME

 Reliance on a bank or portion thereof to be released to prevent undesired consequences to a living resource requires a bewildering ability to be able to predict the time, duration, and amount of water that needs to be released, and is dependent upon many unknown or unpredictable conditions and effects.  For example, if a reservoir is spilling and water is being withdrawn (diverted) from the system, the manager needs to be able to predict the effect such withdrawal will have on the amount being spilled and the rate at which the amount that is spilling will change during the release.  He needs to be able to predict how much the water will be heated by exposed rocks during transit time (a function of existing flow and weather) and how long it will take to reach the target (a function of amount of release, distance to target, and the existing flow before release).  Releases from major tributaries such as the Lackawaxen River and Mongaup are highly unpredictable but profoundly effect the flow at Montague, N. J.

  AIR TEMPERATURE AND CLOUD COVER

 Although the air temperature is an important factor, the greatest heat gain to a river system occurs by the absorption of sunlight by the rocks in the bottom of the stream, especially on shallow riffles.  Even on comparatively cool days, when the sun is high in the sky, as in June, a great amount of solar energy is absorbed by the rocks through the relatively transparent water and then conducted to the water from below.  Although part of this prediction can be inferred by weather forecasts, there can be considerable variation from day to day and is highly unpredictable.  The amount of heat that is absorbed by the substrate changes throughout the summer, being greatest in June when the sun is highest in the sky and then decreases throughout the summer, as air temperatures climb.  Consequently the water temperatures in the designated trout management sections rise and fall rapidly and sporadically throughout the summer on a daily basis.

. ASSUMPTIONS

 A system based on temperature and flow targets assumes that the temperature and flow targets chosen are biologically important to the target organisms and that these targets reflect optimum conditions for the entire system, not just at the target location.  Because the trout are able to move and their behavior is strongly affected by water depth, velocity and temperature, all of which vary widely throughout the entire system, the ability to calculate a specific set of temperature and flow criteria, best for the trout fishery, let alone the complex array of aquatic organisms that may have important ecological significance, is highly problematic at best.  It is by no means given that in a system as large and complex as the Delaware River that any such combination of temperature and flow targets could ever be judged as being best for the system as a whole.

 Temperature targets of 72F and 75 F are based on mortality rates of individual trout held in isolation.  They are not intended to, nor do they adequately reflect the impact on the ecosystem much less the various populations of wild trout.  Temperature strongly affects not only the physiology of trout but their behavior as well.  Above 68 F, trout can no longer feed efficiently.  At this temperature trout begin to move in search of cooler water.  This movement affects the social hierarchy of the trout and causes excess expenditure of energy just at the time at which the fish can no longer feed efficiently.  If temperatures are allowed to gradually increase and flows are not artificially changed over an unpredictable and erratic period the trout will instinctively move in search of cool water.  This may be upstream, or even downstream if coldwater refuges exist downstream at nearby springs or tributaries.

 ASSUMPTION THAT PULSED RELEASES ARE BENEFICIAL TO THE TROUT

 If the water is artificially and temporally lowered the behavior of the trout is unnaturally altered to the detriment of the population as a whole.  Instead of moving to cooler water, the trout may be temporarily induced to stay in a potentially lethal location.  Then, when the flows are reduced and temperatures once again begin to rise, the trout may not be able to negotiate shallow riffle areas in search of cooler water.  Sudden and brief pulses of cold water in a lotic (running water) environment are unnatural and are found nowhere in a natural system.  No aquatic organisms have ever been exposed to such an environment naturally and therefore have never become adapted to cope with such conditions.  Pulses of cold water cause fish and invertebrates to behave unnaturally and undoubtedly to the detriment of both.

 ASSUMPTION THAT THE DROUGHT OF RECORD STARTS TOMORROW

 The easiest way to reduce the risk of running out of water is to assume the drought of record starts tomorrow.  But a fisheries management plan that is subject to such a constraint necessarily constrains the ecosystem to permanent drought conditions.  In natural systems, aquatic organisms undergo periods of scarcity and abundance depending on the weather that particular year.  A system based on the most extreme drought conditions condemns the ecosystem to perpetual drought regardless of the actual climatic conditions.

 ENFORCEABILITY

 Temperature and flow targets are just that, targets.  They are not mandatory requirements, and require a good-faith willingness to be met.  Failure to meet such targets carries with them no consequences other than the impact on the resource.  To be effective, such a system needs to carry with it the force of law with penalties for failure of adherence.  It is unlikely that any system that relies on so many variables, unknowns, day to day monitoring and un-testable assumptions could ever gain the authority of law or regulation.

 AN ALTERNATIVE

A SYSTEM BASED ON AVAILABILITY OF WATER ON A REAL-TIME BASIS AND ACCEPTABLE RISK, IN WHICH A SPECIFIED AMOUNT OF WATER IS RELEASED AS A FUNCTION OF STORAGE AND TIME OF YEAR (PROBABILITY OF REFILL) ELIMINATES VIRTUALLY ALL OF THE “PROBLEMS” DISCUSSED ABOVE.   SUCH A SYSTEM NEED NOT INCREASE THE FREQUENCY OR PROBABILITY OF “DROUGHT”, IS MUCH MORE BENEFICIAL TO THE AQUATIC ORGANISMS IN THE RIVER AND IS   EASY TO IMPLEMENT.    

GIVE THE AQUATIC ORGANISMS THE AMOUNT OF WATER THAT IS AVAILABLE TODAY AND THEY WILL TAKE CARE OF THEMSELVES.

 

Robert Bachman, Ph.D

 

Home / Leadership / Objectives / Accomplishments / Facts / Join /   Get Involved /  Endorsements  /  Contact Us

 FUDR  :: 1148 5th St., New York, NY 10128::  email: catskilldan@mac.com ::  607-363-2001