يعد تلوث المياه الجوفية بالنترات مشكلة شائعة في العديد من دول العالم وبخاصة الزراعية منها حيث ينشأ التلوث في هذه البلدان بشكل أساسي من الاستخدام الزائد للتسميد في المناطق الزراعية ومن النفايات الصناعية والصرف الصحي وروث الحيوانات، وأيضا" من التثبيت الجوي للنتروجين بواسطة النباتات، بالإضافة إلى مركبات النتروجين التي تنشأ بفعل بعض الصناعات وانبعاثات السيارات وتترسب على الأرض بشكل مواد صلبة. وتعد النترات من المركبات المسرطنة والخطرة على الصحة البشرية إذا ما وجدت بتراكيز مرتفعة، وتأتي هذه الخطورة من تحول النترات الممتص إلى نتريت بفعل بكتريا خاصة في البطن والذي يسبب بدوره ما يعرف بالميثموغلوبينيميا لدى الرضع والحوامل (مرض ازرقاق الرضع ) كما يمكن أن يسبب سرطان المعدة لدى البالغين عبر تفاعله مع الأمينات والأميدات في البطن مشكلاً مواد مسرطنة (النتروزأميدات والنترزوأمينات)، لذلك يجب تطبيق أسس الإدارة المتكاملة للمياه الجوفية في منطقة الدراسة والمحافظة على مستويات منخفضة للنترات في المياه الجوفية المستخدمة للشرب وللري .
The contamination of groundwater with nitrates is a common problem in many countries of
the world, especially the agricultural ones where the pollution originates in these countries
mainly from the use of excessive fertilization in agricultural areas, industrial waste,
sewage, animal dung, and the "installation of air nitrogen by plants, the nitrogen
compounds that arise due to some industries and vehicle emissions which are deposited on
the ground in solids.
The nitrate compounds are carcinogens and hazardous to human health If they were in
high concentrations. The risk of this turning into nitrite nitrate uptake by the bacteria,
especially in the abdomen which in turn causes what is known as Balmithmoglubenemea
in infants and pregnant women (Infant disease blueness). It can also cause stomach cancer
in adults through its interaction with amines and amides in the abdomen, forming
carcinogens (Alntrozzomedat and Alentrzoaminat). Therefore, you must apply the
foundations of the integrated management of groundwater in the study area to maintain
low levels of nitrate in groundwater used for drinking and irrigation.
References used
JOHN, E. B. Environmental Reauthorization and Regulatory , National Library for Environment, U.S.A. 96-949, 1998
UN . Environment and Development. Rio De Janeiro, 1992, 54
GEORGE, M. Dose – Response Relationship : Principles of Environmental Toxicology. University of Idaho , U.S.A. 2002, 1-32
WHO . Mercury in Drinking Water , Background Document of Guidelines for Drinking Water Quality. WSH, U.S.A. 2005, 18
CURTIS, A. B. Health risk analysis of groundwater nitrate contamination. PHD research , university of Nebraska Lincoln, U.S.A. 2002, 66-143
Barada and Auvage basin, experience of limited water resources against
growing of human activities related to increasing of inhabitants, and climate
changes influence on precipitation and water balance. This research focuses on
the definition of p
Biological Denitrification process in anoxic fluidized bed reactor is a simple
way to eliminate nitrate – nitrogen that pollute the groundwater.
In this method the biofilm (including organic bacteria) was cultured on the
reactor bed particles, whi
An available free groundwater were classified
hydrochemical, and determined its fitting for general uses in a part
of Damascus's Ghouta, which suffers water deficiency, where the
study carried out on groundwater samples taken from 20 wells
distri
This study was carried out on 90 broiler chicks which divided into three groups. The first group has been given 0.75 g/L potassium nitrate and the second group was given 1 g/L potassium nitrate with drinking water for 30 days, While the third group w
Natural changes in the level of ground water through time is gaining great
importance in evaluating the water system and to provide a lot of information about
groundwater movement , which allows the assessment of the water situation public water
l