(function(){"use strict";var $=jQuery;var debug=false;var elements={};var selection={wasserwerk:null};var initSettings={autoSelectFirst:false,unfoldOnLoad:false,foldAfterSelect:false,isFolded:true,autoSelectOrt:'',autoSelectWasserwerk:''};var globals={};var flyoverTimer=null;var renderFunctions={HEADLINE:function(){$HTML("div",{parentNode:elements.main,classList:["row","twa-header"],childNodes:[$HTML("div",{classList:["col-xs-12"],childNodes:[$HTML(config.settings.header.level1,{classList:["twa-header-level1","my-4","color-blue","hl-m","hl-md-l","hl-lg-xl"],textContent:config.text[globals.ortID].title}),$HTML("a",{classList:["link"]}),]}),$HTML("div",{classList:["col-xs-12"],childNodes:[$HTML("p",{classList:["twa-bodytext"],innerHTML:config.text[globals.ortID].description})]})]});},SELECTOR:function(){$HTML("div",{parentNode:elements.main,classList:["row","twa-wasserwerk-auswahl"],childNodes:[$HTML("div",{classList:["col-xs-12"],childNodes:[elements.wasserwerke]})]});},OVERVIEW:function(){overview.generateHeader();},INTRO:function(){details.generate(globals.ortID);},TABLE:function(){wasserwerke.generateData(globals.firstID);elements.main.appendChild($HTML("div",{classList:["row","twa-table"],childNodes:[$HTML("span",{id:"twa-breakpoint-xs",classList:["visible-xs","d-block","d-sm-none"]}),elements.table]}));},DOWNLOADS:function(){downloads.generate(globals.ortID);}};var view={render:function(ortID){var i,item,firstID;$CLEAR(elements.main);elements.overview=$HTML("div",{classList:["twa-overview"],});elements.wasserwerke=$HTML("div",{classList:["row"]});elements.table=$HTML("div",{classList:["col-xs-12"],childNodes:[$HTML("span",{id:"twa-breakpoint-xs",classList:["visible-xs","d-block","d-sm-none"]})]});selection.wasserwerk=null;globals={firstID:wasserwerke.generate(ortID),ortID:ortID};for(i=0;i<config.settings.view.length;i++){item=config.settings.view[i];if(renderFunctions.hasOwnProperty(item)){renderFunctions[item].call();}}
if(initSettings.foldAfterSelect){list.fold(true);}
flyover.generate(ortID);}};var list={generate:function(listType,moreElements){if(elements[listType]){var i;if(moreElements){for(i=0;i<moreElements.length;i++){list.addElement[listType](" ",moreElements[i]);}}
for(i=0;i<config.orte.length;i++){list.addElement[listType](config.orte[i].id,config.orte[i].ort);}}},fold:function(isFolded){if(elements.div){var i;isFolded=!(isFolded===false);$(elements.div).find('*').slideDown();elements.div.childNodes[0].style.display=(isFolded?'block':'none');for(i=1;i<elements.div.childNodes.length;i++){elements.div.childNodes[i].style.display=(isFolded?'none':'block');}
initSettings.isFolded=isFolded;elements.div.classList[isFolded?'add':'remove']('twa-folded');}},selectOrt:function(ortID){var i;if((ortID!=" ")&&(config.map_orte_wasserwerke.hasOwnProperty(ortID))){if(elements.select){for(i=0;i<elements.select.options.length;i++){if(elements.select.options[i].value===ortID){elements.select.selectedIndex=i;break;}}}
if(elements.ul){for(i=0;i<elements.ul.childNodes.length;i++){$(elements.ul.childNodes[i]).removeClass('twa-selected').removeClass(config.settings.class.selected.ort);if($DATA(elements.ul.childNodes[i],'twaOrtId')===ortID){$(elements.ul.childNodes[i]).addClass('twa-selected').addClass(config.settings.class.selected.ort);}}}
if(elements.div){for(i=0;i<elements.div.childNodes.length;i++){$(elements.div.childNodes[i]).removeClass('twa-selected').removeClass(config.settings.class.selected.ort);if($DATA(elements.div.childNodes[i],'twaOrtId')===ortID){$(elements.div.childNodes[i]).addClass('twa-selected').addClass(config.settings.class.selected.ort);}}}
view.render(ortID);return true;}
return false;},addElement:{select:function(id,text){elements.select.add($HTML("option",{value:id,textContent:text}));},ul:function(id,text){elements.ul.appendChild($HTML("li",{childNodes:[$HTML("a",{textContent:text,href:'#',events:{click:function(event){list.selectOrt(id);event.preventDefault();}}})],data:{twaOrtId:id},}));},div:function(id,text){elements.div.appendChild($HTML("div",{classList:["col-xs-6","col-md-4","col-lg-3","link-icon--arrow","link-icon","link","util-block","my-2","js-filter-item"],childNodes:[$HTML("a",{textContent:text,href:'#',events:{click:function(event){if(id!=" "){list.selectOrt(id);}else{list.fold(false);}
event.preventDefault();}}})],data:{twaOrtId:id},}));}},clear:{select:function(id,text){while(elements.select.options.length>0){elements.select.remove(0);}},ul:function(id,text){$CLEAR(elements.ul);},div:function(id,text){$CLEAR(elements.div);}}};var wasserwerke={generate:function(ortID){var i,liste,firstID,wasserwerk,colSize;liste=config.map_orte_wasserwerke[ortID];colSize=Math.floor(12 / config.map_orte_wasserwerke[ortID].length);if(colSize<2){colSize=2;}
if(colSize>3){colSize=3;}
for(i=0;i<config.map_orte_wasserwerke[ortID].length;i++){wasserwerk=config.wasserwerke[config.map_orte_wasserwerke[ortID][i]];if(selection.wasserwerk===null){selection.wasserwerk=wasserwerk.id;firstID=selection.wasserwerk;}
(function(){var wasserwerkData;wasserwerkData=wasserwerk;$HTML("div",{classList:['col-md-'+colSize,'col-sm-6','col-xs-12','text-center','twa-wasserwerk-container'],parentNode:elements.wasserwerke,childNodes:[$HTML("div",{id:'twa-wasserwerk-'+wasserwerkData.id,textContent:wasserwerkData.wasserwerk,classList:(selection.wasserwerk===wasserwerkData.id)?['twa-wasserwerk','twa-selected',config.settings.class.selected.wasserwerk]:['twa-wasserwerk'],data:{twaWasserwerkId:wasserwerkData.id},events:{click:function(){$('#twa-wasserwerk-'+selection.wasserwerk).removeClass('twa-selected').removeClass(config.settings.class.selected.wasserwerk);selection.wasserwerk=wasserwerkData.id;$('#twa-wasserwerk-'+selection.wasserwerk).addClass('twa-selected').addClass(config.settings.class.selected.wasserwerk);wasserwerke.generateData(wasserwerkData.id);}}})]});})();}
return firstID;},generateData:function(wasserwerkID){table.generate(wasserwerkID);overview.generate(wasserwerkID);}};var downloads={generate:function(ortID){$HTML("div",{parentNode:elements.main,classList:["row","twa-downloads","twa-downloads--pdf"],childNodes:$CONCAT([$HTML("div",{classList:['col-xs-12'],childNodes:[$HTML(config.settings.header.level2,{classList:["twa-header-level2"],textContent:config.data.text.titles.downloads})]})],(function(){var downloadList,resultList,i;downloadList=config.downloads[ortID];resultList=[];try{for(i=0;i<downloadList.length;i++){resultList.push($HTML("div",{classList:["col-md-6","col-xs-12"],childNodes:$CONCAT([$HTML(config.settings.header.level3,{classList:["twa-header-level3"],textContent:downloadList[i].title})],downloads.generateLinks(downloadList[i].files))}));}}catch(e){$LOG('No downloads available for the selected item: <ortID:'+ortID+'>','WARNING');}
return resultList;})())});},generateLinks:function(fileList){var resultList,i;resultList=[];for(i=0;i<fileList.length;i++){resultList.push($HTML("div",{classList:["col-xs-12"],childNodes:[$HTML("a",{classList:["twa-download"],href:fileList[i].url,target:"_blank",textContent:fileList[i].title}),$TEXT(' ('+fileList[i].type+', '+fileList[i].size+')'),]}));}
return resultList;}};var overview={generateHeader:function(){$HTML("div",{parentNode:elements.main,classList:["row"],childNodes:[$HTML("div",{classList:["col-xs-12"],childNodes:[$HTML(config.settings.header.level2,{classList:["twa-header-level2"],textContent:config.data.text.titles.ueberblick}),]}),$HTML("div",{classList:["col-xs-12"],childNodes:[elements.overview]})]});},generate:function(wasserwerkID){if(config.analyse[wasserwerkID]){$CLEAR(elements.overview);$HTML("div",{parentNode:elements.overview,classList:["row"],childNodes:overview.generateItems(config.analyse[wasserwerkID].ueberblick)});}else{$LOG('No detail information available for the selected item: <wasserwerkID:'+wasserwerkID+'>','WARNING');}},generateItems:function(itemList){var list,i;list=[];for(i=0;i<itemList.length;i++){list.push($HTML("div",{classList:['col-md-2','col-sm-3','col-xs-6','text-center','twa-item'],childNodes:[$HTML("div",{classList:["text-uppercase","twa-item-header"],textContent:itemList[i].title}),$HTML("div",{classList:(itemList[i].special)?["twa-item-body","twa-no-unity"]:["twa-item-body"],childNodes:(function(){var ch=[];ch.push($HTML("div",{classList:["twa-item-value"],textContent:itemList[i].value,style:itemList[i].style}));ch.push($HTML("div",{classList:["twa-item-unity"],textContent:itemList[i].unit}));if(itemList[i].limit!=''){ch.push($HTML("div",{classList:["small","twa-item-limit"],innerHTML:((itemList[i].unit!='')?config.data.text.limit+':<br/>'+((itemList[i].limit!='')?itemList[i].limit:'-/-'):'')}));}
return ch;})()}),]}))}
return list;}};var details={generate:function(ortID){$HTML("div",{parentNode:elements.main,classList:["row","twa-details"],childNodes:[$HTML("div",{classList:["col-xs-12"],childNodes:[$HTML(config.settings.header.level2,{classList:["twa-header-level2"],textContent:config.data.text.titles.details}),$HTML("p",{classList:["twa-bodytext"],innerHTML:config.data.text.intro.replace(/<p class=\"bodytext\">&nbsp;<\/p>/g,"")})]})]});}};var table={generate:function(wasserwerkID){var tables,i;try{$CLEAR(elements.table);tables=config.analyse[wasserwerkID].tables;for(i=0;i<tables.length;i++){elements.table.appendChild(table.generateTableItem(tables[i]));}}catch(e){$LOG('No analysis data available for the selected item: <wasserwerkID:'+wasserwerkID+'>','WARNING');}
if(elements.wasserwerke){for(i=0;i<elements.wasserwerke.childNodes.length;i++){$(elements.wasserwerke.childNodes[i]).removeClass('twa-selected').removeClass(config.settings.class.selected.wasserwerk)
if($DATA(elements.wasserwerke.childNodes[i],'twaWasserwerkId')===wasserwerkID){$(elements.wasserwerke.childNodes[i]).addClass('twa-selected').addClass(config.settings.class.selected.wasserwerk);}}}},generateSubTables:function(subtables){var list,i,content;list=[];for(i=0;i<subtables.length;i++){content=table.generateSubTableItemContent(subtables[i]);list.push(table.generateSubTableItemHeader(subtables[i],content));list.push(content);}
return list;},generateTableItem:function(tableData){var contentDiv,link;link=$HTML("a",{classList:["twa-toggle","twa-folded"],innerHTML:config.data.text.table.titles[tableData.id]});contentDiv=$HTML("div",{classList:["twa-panel-content"],style:'display:none;',childNodes:[$HTML("div",{classList:["twa-panel-body"],childNodes:(tableData.subtables?[$HTML("div",{childNodes:$CONCAT([$HTML("div",{classList:[],childNodes:[$HTML("p",{classList:["twa-bodytext"],innerHTML:config.data.text.table.descriptions[tableData.id]})]})],table.generateSubTables(tableData.subtables))})]:[table.generateTableContent(tableData)])})]});return $HTML("div",{classList:["twa-panel"],childNodes:[$HTML("div",{classList:["twa-panel-heading","twa-folded"],events:{click:function(){$(this).toggleClass('twa-folded');if($(this).hasClass('twa-folded')){$(link).addClass('twa-folded');$(contentDiv).slideUp();}else{$(link).removeClass('twa-folded');$(contentDiv).slideDown();}},mousemove:function(){if(!$('#twa-breakpoint-xs').is(':visible')&&$('.twa_loading').attr('data-prevent-flyover')!='true'){flyover.show(this);}},mouseout:function(){if(!$('#twa-breakpoint-xs').is(':visible')){}}},childNodes:[$HTML("div",{childNodes:[$HTML(config.settings.header.level3,{classList:["twa-panel-title","twa-header-level3"],childNodes:[link]})]})]}),contentDiv]});},generateSubTableItemHeader:function(subtableData,contentDiv){var link;link=$HTML("a",{classList:["twa-toggle","twa-folded"],innerHTML:config.data.text.table.titles[subtableData.id]});return $HTML("div",{classList:["twa-panel"],childNodes:[$HTML("div",{classList:["twa-panel-heading","twa-folded"],events:{click:function(){$(this).toggleClass('twa-folded');if($(this).hasClass('twa-folded')){$(link).addClass('twa-folded');$(contentDiv).slideUp();}else{$(link).removeClass('twa-folded');$(contentDiv).slideDown();}}},childNodes:[$HTML("div",{childNodes:[$HTML(config.settings.header.level3,{classList:["twa-panel-title","twa-header-level3"],childNodes:[link]})]})]})]});},generateSubTableItemContent:function(subtableData){return $HTML("div",{classList:["twa-panel-content"],style:'display:none;',childNodes:[$HTML("div",{classList:[],childNodes:[$HTML("p",{classList:["twa-bodytext"],innerHTML:config.data.text.table.descriptions[subtableData.id]}),]}),$HTML("table",{classList:["twa-table"],childNodes:[$HTML("thead",{classList:["twa-thead"],childNodes:[$HTML("tr",{classList:["twa-tr"],childNodes:table.generateHeader(subtableData.columns)})]}),$HTML("tbody",{classList:["twa-tbody"],childNodes:table.generateData(subtableData.data,subtableData.columns)})]})]});},generateTableContent:function(tableData){return $HTML("div",{childNodes:[$HTML("div",{classList:["small-table"],childNodes:[$HTML("div",{classList:[],childNodes:[$HTML("p",{classList:["twa-bodytext"],innerHTML:config.data.text.table.descriptions[tableData.id]})]}),$HTML("table",{classList:["twa-table"],childNodes:[$HTML("thead",{classList:["twa-thead"],childNodes:[$HTML("tr",{classList:["twa-tr"],childNodes:table.generateHeader(tableData.columns)})]}),$HTML("tbody",{classList:["twa-tbody"],childNodes:table.generateData(tableData.data,tableData.columns,tableData.data)})]})]})]});},generateHeader:function(headerList){var i,lst;lst=[];for(i=0;i<headerList.length;i++){lst.push($HTML("th",{classList:["twa-th","text-uppercase","twa-th-"+headerList[i]],innerHTML:config.data.text.table.columns[headerList[i]]}));}
return lst;},generateData:function(dataList,headerList){var i,lst;lst=[];for(i=0;i<dataList.length;i++){lst.push($HTML("tr",{classList:[(((i%2)===0)?'twa-tr-odd':'twa-tr-even')],childNodes:(function(){var chList,j,tdSettings;chList=[];for(j=0;j<dataList[i].data.length;j++){tdSettings={classList:["twa-td",headerList[j]],data:{'th':config.data.text.table.columns[headerList[j]].replace('- ','').replace('<br\/>',' ')},childNodes:(function(){if((j==0)&&dataList[i].metadata){return[$HTML("i",{classList:['twa-info-circle'],data:{title:dataList[i].data[dataList[i].metadata.title],tooltip:dataList[i].metadata.tooltip},events:{mouseover:function(event){tooltip.show(event.pageX-$(window).scrollLeft(),event.pageY-$(window).scrollTop(),$(this).data('title'),$(this).data('tooltip'));},mouseout:function(){tooltip.hide();}}})];}else{return[];}})()};tdSettings.textContent=dataList[i].data[j];if(!tdSettings.textContent){tdSettings.innerHTML='&nbsp;';}
chList.push($HTML("td",tdSettings));}
return chList;})()}));}
return lst;},};var tooltip={show:function(posX,posY,title,text){$(elements.tooltip).addClass('twa-visible').empty().append($HTML("div",{classList:['twa-tooltip-header'],textContent:title})).append($HTML("div",{classList:['twa-tooltip-text'],innerHTML:text}))
elements.tooltip.style.left=posX+'px';elements.tooltip.style.top=posY+'px';},hide:function(){$(elements.tooltip).removeClass('twa-visible');}};var flyover={generate:function(ortID){var i,info;$CLEAR(elements.flyover);for(i=0;i<config.data.infobox.length;i++){(function(){var j,info,ul,items;info=config.data.infobox[i];$HTML("div",{classList:["twa-flyover-header"],parentNode:elements.flyover,textContent:info.title,events:{click:function(event){event.stopPropagation();ul.toggleClass('twa-unfolded');if(ul.hasClass('twa-unfolded')){ul.slideDown();}else{ul.slideUp();}}}});if(info.type=='foldList'){items=[];for(j=0;j<info.entries.length;j++){items.push($HTML("li",{childNodes:(function(){var divTitle,divText;divTitle=$HTML("div",{classList:["twa-flyover-content-header"],innerHTML:info.entries[j].title,events:{click:function(){$(divText).toggleClass('twa-unfolded');if($(divText).hasClass('twa-unfolded')){$(divTitle).addClass('twa-unfolded');$(divText).slideDown();}else{$(divTitle).removeClass('twa-unfolded');$(divText).slideUp();}}}});divText=$HTML("div",{classList:["twa-flyover-content-text"],innerHTML:info.entries[j].text});return[divTitle,divText];})()}));}}else
if(info.type=='linkList'){items=[];for(j=0;j<info.entries.length;j++){items.push($HTML("li",{childNodes:[$HTML("a",{classList:["twa-flyover-link"],textContent:info.entries[j].title,href:info.entries[j].url,target:'_blank'})]}));}}else
if((info.type=='downloadList')||(info.title.toLowerCase()=='downloads')){items=[];info.type='downloadList';for(j=0;j<config.downloads[ortID].length;j++){items.push($HTML("li",{childNodes:[$HTML("div",{classList:["twa-flyover-download-title"],textContent:config.downloads[ortID][j].title,childNodes:(function(){var lst,k;lst=[];for(k=0;k<config.downloads[ortID][j].files.length;k++){lst.push($HTML("div",{childNodes:[$HTML("a",{classList:["twa-flyover-link"],textContent:config.downloads[ortID][j].files[k].title,href:config.downloads[ortID][j].files[k].url,target:'_blank'}),$HTML("span",{classList:["twa-flyover-link-details"],textContent:' ('+config.downloads[ortID][j].files[k].type+', '+config.downloads[ortID][j].files[k].size+')',href:config.downloads[ortID][j].files[k].url,target:'_blank'})]}))}
return lst;})()})]}));}}
ul=$($HTML("ul",{classList:["twa-flyover-ul","twa-"+info.type],parentNode:elements.flyover,childNodes:items}));})();}},show:function(parentNode){try{clearTimeout(flyoverTimer);}catch(ignore){};$(elements.flyover).addClass('twa-visible');if(parentNode&&elements.flyover.parentNode!=parentNode){$(parentNode).append(elements.flyover);}},hide:function(){try{clearTimeout(flyoverTimer);}catch(ignore){};flyoverTimer=setTimeout(function(){$(elements.flyover).removeClass('twa-visible');$(elements.flyover).find('.twa-flyover-ul, .twa-flyover-content-text').removeClass('twa-unfolded').slideUp();$(elements.flyover).find('.twa-flyover-content-header').removeClass('twa-unfolded');$('#twa_Analysedaten_Content').append(elements.flyover);},500);}}
var dom={clearElement:function(element){while(element.hasChildNodes()){element.removeChild(element.firstChild);}},createElement:function(name,attributes){var el,i,attrList,styleElements,styleValues;attrList=['id','value','href','target','textContent','innerHTML'];el=document.createElement(name);if(attributes){for(i=0;i<attrList.length;i++){if(attributes[attrList[i]]){el[attrList[i]]=attributes[attrList[i]];}}
if(attributes.style){styleElements=attributes.style.split(';');for(i=0;i<styleElements.length;i++){styleValues=styleElements[i].split(':',2);$(el).css(styleValues[0],styleValues[1]);}}
if(attributes.events){for(i in attributes.events){$EVENT(el,i,attributes.events[i]);}}
if(attributes.data){for(i in attributes.data){el.dataset[i]=attributes.data[i];}}
if(attributes.classList){for(i=0;i<attributes.classList.length;i++){el.classList.add(attributes.classList[i]);}}
if(attributes.childNodes){for(i=0;i<attributes.childNodes.length;i++){el.appendChild(attributes.childNodes[i]);}}
if(attributes.parentNode){attributes.parentNode.appendChild(el);}}
return el;},createTextNode:function(text){return document.createTextNode(text);},registerEvent:function(element,eventType,handler){$(element).on(eventType,handler);},getData:function(element,attribute,convertToLowerCase){convertToLowerCase=(convertToLowerCase===true);if(element.dataset[attribute]){try{if(convertToLowerCase){return element.dataset[attribute].toLowerCase();}else{return element.dataset[attribute];}}catch(ignore){}}
return'';}};var utility={isInList:function(elem,list){var i;for(i=0;i<list.length;i++){if(list[i]==elem){return true;}}
return false;},concatLists:function(list1,list2){var i,resultList;resultList=[];try{for(i=0;i<list1.length;i++){resultList.push(list1[i]);}
for(i=0;i<list2.length;i++){resultList.push(list2[i]);}}catch(ignore){}
return resultList;},logMessage:function(text,type,object){if(debug){if(!type){type='DEBUG';}
console.log('[TWA:'+type+'] '+text);if(object){console.log(object);}}}};var $HTML=dom.createElement;var $TEXT=dom.createTextNode;var $EVENT=dom.registerEvent;var $CLEAR=dom.clearElement;var $DATA=dom.getData;var $CONCAT=utility.concatLists;var $LOG=utility.logMessage;var config={"settings":{"clientID":["http:\/\/v83859.wasserwerke-westfalen.de","https:\/\/www.wasserwerke-westfalen.de","http:\/\/www.wasserwerke-westfalen.de","https:\/\/www.gelsenwasser.de","http:\/\/twa.vancado.develop","http:\/\/update.gw.gwag.top"],"elementIDs":{"select":"twa_Orte_SelectBox","ul":"twa_Orte_LinkList","div":"twa_Orte_DynamicList","main":"twa_Analysedaten_Content"},"class":{"table":["contenttable","tx_gwtrinkwasseranalyse","table"],"tr_head":["tw-table","header"],"tr":[],"th":[],"td":[],"selected":{"ort":"selected","wasserwerk":"selected"}},"header":{"level1":"h2","level2":"h3","level3":"h4"}},"data":{"text":{"limit":"Grenzwert","einenAnderenOrtWaehlen":"Einen anderen Ort ausw\u00e4hlen...","ortAuswaehlen":"Ort ausw\u00e4hlen...","titles":{"downloads":"Jahresanalyse","ueberblick":"In aller K\u00fcrze","details":"Detailanalyse"},"intro":"<p class=\"bodytext\"> F\u00fcr Ihre Sicherheit \u00fcberpr\u00fcft die Wasserwerke Westfalen GmbH das Trinkwasser mehrmals t\u00e4glich. Pro Jahr werden so mehrere Tausend Wasserproben zur Analyse ins Labor geschickt. Die Westf\u00e4lische Wasser- und Umweltanalytik GmbH (WWU) ist als akkreditierte Untersuchungsstelle von der Wasserwerke Westfalen GmbH mit der Trink- und Rohwasser\u00fcberwachung beauftragt. Einen geringen Teil der Analysen vergibt die WWU als Unterauftrag an renommierte Untersuchungsstellen wie z. B. das Hygiene-Institut des Ruhrgebiets in Gelsenkirchen.\n<\/p>\n<h3> In aller Tiefe \u2013 f\u00fcr alle, die mehr wissen wollen<\/h3>\n<p class=\"bodytext\"> Die Diskussionen \u00fcber Spurenstoffe haben deutlich gemacht, dass bei unseren Kunden ein gro\u00dfes Interesse daran besteht zu erfahren, wie das gelieferte Trinkwasser beschaffen ist. Die Wasserwerke Westfalen GmbH hat sich darum entschlossen - \u00fcber die gesetzlichen Ver\u00f6ffentlichungspflichten hinaus - die Erkenntnisse aus der immer feiner messenden Analytik weiterzugeben. Die nachfolgend tabellarisch zusammengestellten Analysen basieren auf Untersuchungsergebnissen der Westf\u00e4lischen Wasser- und Umweltanalytik GmbH (WWU).\n<\/p>\n<p class=\"bodytext\">&nbsp;<\/p>\n<p class=\"bodytext\">&nbsp;<\/p>","table":{"titles":{"allgemein":"Allgemeine Parameter","kationen":"Kationen","anionen":"Anionen","metalle":"Metalle","org_spurenstoffe":"Organische Spurenstoffe","mikrob_params":"Mikrobiologische Parameter","67a907722bbbc32dc135a47012e9962e":"Arzneistoffe und deren Metabolite","3f6dd20eb5a608776ee8039ca4bc0bd7":"Benzotriazole","2dc7583c2ce40a92854487fd20c28913":"Flammschutzmittel","18da6e8692e56587d294b7544fdaf0dd":"Komplexbildner","f827e4307c3b81ec511903ab19ab9c2f":"Leichtfl\u00fcchtige aromatische Kohlenwasserstoffe (BTEX)","251dbf71627cf8de5d9249b5d758c383":"Leichtfl\u00fcchtige Kohlenwasserstoffe (u.a. LHKW)","5a306064af653463d16f5508990cf969":"L\u00f6semittel","6387669ee20a359dd2c175607d1ba1a2":"Nitrosamine","69b635fc280bdf69f9e1ea3074398310":"Perfluorierte Verbindungen","3889373f90beed1ca2d059b1a029b27a":"Pflanzenschutzmittel (PSM)","7e14beef3c6c130718341c4170fbc240":"Pflanzenschutzmittel-Metabolite","973ebf7897703138e7089dd642923f8b":"Polyzyklische Aromatische Kohlenwasserstoffe","2b04f0b0bf376e513761314ca892016a":"S\u00fc\u00dfstoffe","67795c18220c81c9d34c70968d38b0cb":"Trihalogenmethane (THM)","fb1b1f8ec36c036ed71dba94a6a3eb6d":"Umweltchemikalien"},"descriptions":{"allgemein":"Die allgemeinen Parameter beschreiben grundlegend die Qualit\u00e4t eines Wassers und geben z. B. Informationen zu Korrosionseigenschaften (z. B. pH-Wert, Leitf\u00e4higkeit, Calcitl\u00f6sekapazit\u00e4t) und zur H\u00e4rte.","kationen":"Kationen sind positiv geladene Teilchen. Die Stoffe Calcium, Magnesium,  Kalium oder Natrium sind als Mineralstoffe praktisch in jedem Wasser  enthalten. Ammonium, Eisen oder Mangan k\u00f6nnen in Abh\u00e4ngigkeit der  geogenen oder hydraulischen Bedingungen im Einzugsgebiet zwar in h\u00f6heren  Konzentrationen im Rohwasser enthalten sein, werden aber in den meisten  F\u00e4llen bei der Aufbereitung zu Trinkwasser weitgehend entfernt.","anionen":"Die negativ geladenen Teilchen sind die \u201eGegenspieler\u201c der Kationen in  den Mineralsalzen und gemeinsam mit ihnen nicht nur gesundheitlich  bedeutsame Inhaltsstoffe, sondern auch Geschmackstr\u00e4ger f\u00fcr das  Trinkwasser. Bromat, das ebenfalls in diese Gruppe geh\u00f6rt, ist im  Rohwasser im Allgemeinen nicht nachweisbar. Es kann im Zuge der  Wasseraufbereitung als Reaktionsprodukt entstehen und ist mit einem  niedrigen Grenzwert von 0,01 Milligramm pro Liter [mg\/l] belegt.","metalle":"Es ist nicht selten erforderlich im Rohwasser enthaltenes Eisen und  Mangan im Zuge der Trinkwasseraufbereitung zu entfernen. Andere Metalle  und Schwermetalle sind im Trinkwasser \u00fcblicherweise nur in geringsten  Spuren  und h\u00e4ufig gar nicht nachweisbar. F\u00fcr die Hausinstallation von  Interesse sind Kupfer, Nickel, Blei, teilweise auch Cadmium. Diese  Metalle k\u00f6nnen werkstoffbedingt in das Trinkwasser \u00fcbergehen. Bei den  Ergebnistabellen sind die unterschiedlichen Dimensionen (Milligramm pro  Liter [mg\/l], Mikrogramm pro Liter [\u00b5g\/l]) zu beachten.","org_spurenstoffe":"In der Gruppe der organischen Spurenstoffe sind Substanzen unterschiedlicher chemischer Zugeh\u00f6rigkeiten zusammengefasst. Gemeinsam ist ihnen, dass sie soweit \u00fcberhaupt vorhanden, im Allgemeinen nur in sehr niedrigen Konzentrationen im Trinkwasser nachweisbar sind. Zur \u00fcbersichtlichen Darstellung der Analysen sind die Einzelkomponenten in den Datentabellen in stoffbezogene Untergruppen unterteilt:","mikrob_params":"Die mikrobiologischen Parameter sind ma\u00dfgebliche Gr\u00f6\u00dfen zur Beurteilung der Trinkwasserqualit\u00e4t. Wichtiges Ziel der Aufbereitung ist es, den bakteriell verwertbaren Anteil an organischen Bestandteilen weitestgehend zu reduzieren. Aus diesem Grunde sollten in Trinkwasserproben nur sehr geringe oder allenfalls moderate Koloniezahlen vorliegen. Coliforme oder E. coli d\u00fcrfen in 100 ml nicht enthalten sein. Einzelne Nachweise kommen gelegentlich vor. Die dann erforderlichen Ma\u00dfnahmen werden immer unverz\u00fcglich mit den Gesundheits\u00e4mtern abgestimmt.","67a907722bbbc32dc135a47012e9962e":"Die Gruppe der Arzneistoffe ist sehr vielf\u00e4ltig. Man unterteilt hier  nicht nach der Chemie der Wirkstoffe, sondern nach der Art der  Anwendungen z. B. R\u00f6ntgenkontrastmittel, Antibiotika, Analgetika,  Antiepileptika, Betablocker. F\u00fcr einige Stoffe wie z.B. das Diclofenac  oder die R\u00f6ntgenkontrastmittel hat das Umweltbundesamt Leitwerte  festgelegt. F\u00fcr die anderen (nicht bewerteten Wirkstoffe) gilt der  strenge Vorsorgewert von 0,1 Mikrogramm pro Liter [\u00b5g\/l].","3f6dd20eb5a608776ee8039ca4bc0bd7":"Benzotriazole werden vielf\u00e4ltig eingesetzt  insbesondere als  Korrosionsschutzmittel in K\u00fchlfl\u00fcssigkeiten und zum Frostschutz. In der  Industrie dienen sie als K\u00fchlschmiermittel bei der Metallbearbeitung.  Ein spezieller Einsatzzweck ist die Verwendung als Enteisungsmittel z.  B. f\u00fcr Flugzeuge. F\u00fcr die Summe der Benzotriazole betr\u00e4gt der  gesundheitliche Orientierungswert (GOW) 3,0 Mikrogramm pro Liter [\u00b5g\/l].","2dc7583c2ce40a92854487fd20c28913":"Flammschutzmittel verhindern oder verlangsamen die Ausbreitung von  Br\u00e4nden (Stoffe, Teppiche, Kleidung etc. aber auch von Ger\u00e4ten). Durch  Auswaschungen k\u00f6nnen sie in die Umwelt gelangen.","18da6e8692e56587d294b7544fdaf0dd":"Komplexbildner werden sehr h\u00e4ufig eingesetzt, um Metall-Ionen in Wasser,  Lebensmitteln und chemischen Produkten in einen f\u00fcr die Verarbeitung  g\u00fcnstigen Zustand zu bringen und die Prozessen besser handhabbar zu  machen. Eintragspfade in die Umwelt sind vor allem Wasch- und  Reinigungsmittel, Produkte der K\u00f6rperhygiene und die Papierherstellung.  F\u00fcr die Summe der Komplexbildner betr\u00e4gt der gesundheitliche  Orientierungswert (GOW) 10 Mikrogramm pro Liter [\u00b5g\/l].","f827e4307c3b81ec511903ab19ab9c2f":"BTEX ist die Abk\u00fcrzung von Benzol, Toluol, Ethylbenzol und Xylol. Als Gruppe zusammengefasst sind es die wichtigsten Vertreter der leichtfl\u00fcchtigen aromatischen Kohlenwasserstoffe. Die Substanzen k\u00f6nnen generell Bestandteil von Erd\u00f6lprodukten sein und sind oft Begleitstoffe von z. B. Polyzyklischen Aromatischen Kohlenwasserstoffen (PAK).","251dbf71627cf8de5d9249b5d758c383":"Die Komponenten dieser Parametergruppe kommen aus unterschiedlichen  Umweltbereichen. 1.2-Dichlorethan ist eine Basis-Chemikalie mit einer  sehr weit verbreiteten Anwendung. Als typische Vertreter der LHKW sind  Methyl-terti\u00e4r-butylether (MTBE) und Ethyl-terti\u00e4r-butylether (ETBE)  h\u00e4ufig in der Umwelt zu finden. Anstelle des fr\u00fcher verwendeten  Tetra-ethyl-Blei werden sie heute dem Benzin als Zuschlagsstoffe  (\u201eAntiklopfmittel\u201c) zugesetzt.","5a306064af653463d16f5508990cf969":"Trichlorethen und Tetrachlorethen werden bei Industrieprozessen und bei  der Textilreinigung vorwiegend als L\u00f6se- und Entfettungsmittel  eingesetzt. Obwohl leichtfl\u00fcchtig k\u00f6nnen sie \u00fcber die industriellen  Anwendungen in die Umwelt gelangen. F\u00fcr die Summe der beiden L\u00f6semittel  betr\u00e4gt der Grenzwert der Trinkwasserverordnung 10 Mikrogramm pro Liter  [\u00b5g\/l].","6387669ee20a359dd2c175607d1ba1a2":"Diese Substanzklasse ist einerseits als Reaktionsprodukt bei  R\u00e4ucherprozessen aus dem Lebensmittelbereich bekannt, Nitrosamine k\u00f6nnen  aber auch aus einer Vielzahl von nitrosierbaren Verbindungen aus dem  chemischen Reaktionsumfeld von Pestiziden, Gummi-Chemikalien,  Arzneimitteln oder Kosmetika gebildet werden. Weiterhin ist bekannt,  dass sie bei der Wasseraufbereitung entstehen k\u00f6nnen, wenn bestimmte  Ausgangsstoffe insbesondere N,N-Dimethylsulfamid (DMS, siehe  Pflanzenschutzmittel-Metabolite) im Rohwasser vorliegen und Ozon bei der  Trinkwasseraufbereitung eingesetzt wird.","69b635fc280bdf69f9e1ea3074398310":"Zu diesen Verbindungen z\u00e4hlen PFC (\u201eperfluorierte Kohlenwasserstoffe\u201c bzw. \u201eperfluorierte Chemikalien\u201c), welche z. B. f\u00fcr Produktionsvorg\u00e4nge in der Galvanikindustrie, zur Herstellung von L\u00f6schsch\u00e4umen und Teflon-beschichteten G\u00fctern verwendet werden. Von Bedeutung sind die PCF auch bei der Herstellung wasserabweisender Kleidung und Papiere. Viele der fluorhaltigen Stoffe sind in der Umwelt schwer abbaubar, dies gilt insbesondere f\u00fcr die Komponenten PFOA (Perfluoroctans\u00e4ure) und PFOS (Perfluoroctansulfons\u00e4ure). Sie werden auch als perfluorierte Tenside \u201ePFT\u201c bezeichnet.","3889373f90beed1ca2d059b1a029b27a":"Pflanzenschutzmittel k\u00f6nnen durch einen nicht bestimmungsgem\u00e4\u00dfen Gebrauch oder ung\u00fcnstige Witterungsbedingungen w\u00e4hrend der Anwendungszeit in die Gew\u00e4sser gelangen. Haupteintragspfad ist die landwirtschaftliche Anwendung. Sch\u00e4dlingsbek\u00e4mpfungsmittel werden beim Land- und Gew\u00e4chshausanbau, als Hilfsmittel gegen Tier- vor allem Insektenbefall und zur Verhinderung von sogenanntem \u201eBiofouling\u201c z. B. in Schutzanstrichen verwendet.","7e14beef3c6c130718341c4170fbc240":"Pflanzenschutzmittelwirkstoffe k\u00f6nnen beim Kontakt mit dem Boden, der Pflanze und dem Wasser abgebaut werden. Die Abbauprodukte dieser Stoffe sind die sogenannten Metabolite. Es handelt sich fast ausschlie\u00dflich um nicht relevante Pflanzenschutzmittel-Metabolite (nach Pflanzenschutzgesetz), die keine Wirkeigenschaften oder toxikologische Relevanz haben.","973ebf7897703138e7089dd642923f8b":"Polyzyklische aromatische Kohlenwasserstoffe (PAK) entstehen bei einer unvollst\u00e4ndigen Verbrennung von organischen Materialien, sind nat\u00fcrlicherweise aber auch in Torf, Kohle oder Roh\u00f6l enthalten. Ein wesentlicher Eintragspfad in die Gew\u00e4sser ist der Abrieb von Teer- bzw. Bitumenoberfl\u00e4chen und die Disposition \u00fcber die Atmosph\u00e4re.","2b04f0b0bf376e513761314ca892016a":"Die globale Verwendung von S\u00fc\u00dfstoffen  im Lebensmittelbereich hat dazu  gef\u00fchrt, dass sie im Spurenbereich in der Umwelt auftreten. S\u00fc\u00dfstoffe  sind toxikologisch unbedenklich. Aufgrund ihrer allgemeinen Verbreitung  sind sie geeignete Indikatoren f\u00fcr menschliche Anwendungen und k\u00f6nnen  f\u00fcr eine umfassende Umweltbewertung herangezogen werden.","67795c18220c81c9d34c70968d38b0cb":"Trihalogenmethane (THM) entstehen regelm\u00e4\u00dfig bei der der Trinkwasserdesinfektion mit Chlor (als Chlorgas oder Hypochlorit) und ihre Bildung muss in diesen F\u00e4llen strikt \u00fcberwacht werden. Sie k\u00f6nnen neben der Desinfektion aber auch durch industrielle Anwendungen gebildet werden.","fb1b1f8ec36c036ed71dba94a6a3eb6d":"In dieser Gruppe sind verschiedene Einzelstoffe oder Stoffgruppen  zusammengefasst, die z.B. im Rahmen einer beh\u00f6rdlichen  Gew\u00e4sser\u00fcberwachung erfasst werden und \u00fcberwiegend aus industriellen  Anwendungen als umweltbelastende Substanzen in die Oberfl\u00e4chengew\u00e4sser  gelangen."},"columns":{"bezeichnung":"Bezeichnung","einheit":"Einheit","jahres_mittel":"Jahres- mittel 2021","min_wert":"Min-Wert<br\/>2021","max_wert":"Max-Wert<br\/>2021","quartalsmittelwert_geo":"Quartals- mittel 4\/2021","grenzwert":"Grenzwert","gow":"Vorsorge- wert"}}},"infobox":[{"title":"Erl\u00e4uterungen","type":"foldList","entries":[{"title":"Informationen zur Analyse ","text":"<p class=\"bodytext\">In den Ergebnistabellen sind die Werte der Labor Analytik parameterweise in Stoffgruppen, teilweise in Untergruppen gegliedert. Aufgef\u00fchrt sind nicht nur die nach Trinkwasserverordnung erforderlichen Analysen, sondern alle Untersuchungsergebnisse des betreffenden Zeitraums. Erg\u00e4nzend untersucht wird dabei insbesondere eine Vielzahl an organischen Spurenstoffen. Diese werden im Allgemeinen nicht aus gesundheitlichen Erw\u00e4gungen analysiert, sondern vorsorglich aus Eigenverantwortung des Unternehmens bzw. aufgrund eines bestehenden \u00f6ffentlichen Interesses. Nicht dargestellt aber f\u00fcr die Kontrolle der Prozesse im Wasserwerk von gro\u00dfer Bedeutung sind die in den Werken installierten kontinuierlich messenden Ger\u00e4te, die wichtige Parameter wie Tr\u00fcbung, Leif\u00e4higkeit und Desinfektionsmittelkonzentration \u00fcberwachen.<\/p>"},{"title":"Zur Orientierung","text":"<p class=\"bodytext\">Zu den Daten gelangt man durch Aufblenden der jeweiligen Gruppen\u00fcberschrift. Bei den organischen Spurenstoffen muss zun\u00e4chst die gew\u00fcnschte Untergruppe angew\u00e4hlt werden. Die Parameter sind in den Daten\u00fcbersichten in alphabetischer Reihenfolge aufgef\u00fchrt, unabh\u00e4ngig von chemisch-strukturellen Verwandtschaften oder Wirkstoff-Eigenschaften. Bei der Beurteilung der Ergebnisse ist zu beachten, dass entsprechend der g\u00e4ngigen Laborpraxis und in Abh\u00e4ngigkeit von den \u00fcblicherweise vorliegenden Konzentrationsbereichen die Analysenwerte entweder in Milligramm pro Liter [mg\/l] oder in Mikrogramm pro Liter [\u00b5g\/l] angegeben sind. Bei Werten in Mikrogramm pro Liter ist die Konzentration 1000-fach geringer als bei Werten in Milligramm pro Liter (siehe Rubrik \u201eMa\u00dfeinheiten\u201c).\n<\/p>\n<p class=\"bodytext\"><b>Aktualisierung der Daten<\/b><br>Die Daten werden in einem Zeitabstand von ca. drei Monaten aktualisiert. \u00dcbertragen werden die Befunde als Quartalsmittelwerte mit einem Zeitverzug von etwa einem Monat. Dieser wird ben\u00f6tigt, damit die Ergebnisse auch f\u00fcr zeitintensive und aufwendig zu analysierende Parameter vollst\u00e4ndig vorliegen. In Ausnahmef\u00e4llen k\u00f6nnen dennoch Werte fehlen, wenn die Ergebnisse aus besonderem Grund nach Ablauf des Monats noch nicht vorliegen.\n<\/p>\n<p class=\"bodytext\"><b>Interpretation der Analysenergebnisse<\/b><br>Zur Beurteilung der Analysenergebnisse sind (soweit vorhanden) die Grenzwerte der Trinkwasserverordnung angegeben. In einer gesonderten Spalte sind (ebenfalls sofern vorhanden) gesundheitliche Vorsorgewerte aufgef\u00fchrt, die das Umweltbundesamt f\u00fcr eine Vielzahl an Spurenstoffen als Leitgr\u00f6\u00dfen zur Bewertung dieser Stoffe formuliert hat. Als Grundlage f\u00fcr die Festlegung von Grenzwerten f\u00fcr chemische Stoffe wird davon ausgegangen, dass eine 75 kg schwere Person 70 Jahre lang t\u00e4glich zwei Liter Wasser zu sich nimmt und zur Ber\u00fccksichtigung anderer Aufnahmequellen (z. B. \u00fcber die Nahrung) der Wert in der Regel noch durch 10 geteilt wird, d. h. 10 % der insgesamt duldbaren Aufnahme aus dem Trinkwasser herr\u00fchren d\u00fcrfen. Weitere Erl\u00e4uterungen hierzu, sowie allgemeine Informationen und Erl\u00e4uterungen zur Darstellung der Analysen und zu den Tabellen, k\u00f6nnen den folgenden Erl\u00e4uterungen sowie der Rubrik&nbsp; Hintergrundinformationen (Link) entnommen werden.<\/p>"},{"title":"Analytische Bestimmungsgrenze","text":"<div id=\"analysegrenze\" class=\"accordion-body collapse in\"><div class=\"accordion-inner\"><p class=\"bodytext\">Die Genauigkeit und Zuverl\u00e4ssigkeit mit der Stoffe analysiert werden k\u00f6nnen, ist wesentlich von der verwendeten Analysenmethode abh\u00e4ngig. Bei der Analytik f\u00fcr die Wasserwerke Westfalen GmbH werden grunds\u00e4tzlich sehr empfindliche, dem aktuellen Stand der Technik entsprechende Bestimmungsverfahren verwendet. <br>Grundlage f\u00fcr die Analytik sind im Allgemeinen vom Normenausschuss Wasser des Deutschen Instituts f\u00fcr Normung e. V. (DIN) herausgegebene Verfahren. Hier treffen sich regelm\u00e4\u00dfig Fachexperten, um abgesicherte Analysenmethoden zu erarbeiten und sie bei Neurungen in der Ger\u00e4tetechnik weiter zu entwickeln. Bei der Anwendung von DIN-Verfahren ist die Vergleichbarkeit der Ergebnisse gegeben und es sind Angaben zur Pr\u00e4zision der Analytik m\u00f6glich. In den letzten Jahren wurden zahlreiche Verfahren speziell f\u00fcr organische Stoffe entwickelt. <br>Wichtige Verfahrensdaten eines Untersuchungsparameters sind \u201eNachweisgrenze\u201c und \u201eBestimmungsgrenze\u201c. Auch wenn es unterschiedliche Ans\u00e4tze gibt, diese Werte zu ermitteln, bedeutet \u201enachweisbar\u201c im Grundsatz stets, dass die Substanz in einer Probe wahrscheinlich enthalten ist. An der Nachweisbarkeits-Schwelle ist die Konzentration aber so gering, dass das Ergebnis nicht zuverl\u00e4ssig angegeben werden kann. Ein \u201e&lt;-Zeichen\u201c vor einem Wert bedeutet, dass die Konzentration geringer ist, als die Bestimmungsgrenze des angewandten Verfahrens und dieses erst oberhalb dieser Konzentration verl\u00e4ssliche Werte liefert.<br>Bei Ergebnissen unterhalb der Bestimmungsgrenze ist unklar, ob die Substanz \u00fcberhaupt in einer Probe enthalten, ob die Gehalte in der N\u00e4he der Bestimmungsgrenze liegen oder ein Wert dazwischen zutrifft. F\u00fcr die Berechnung von Durchschnittswerten sind Festlegungen erforderlich, wie mit Analysen unterhalb der Bestimmungsgrenze verfahren wird. Hierzu gibt es innerhalb der Arbeitsgemeinschaft der Wasserwerke an der Ruhr (AWWR) seit langen Jahren Vereinbarungen, die Wasserwerke Westfalen GmbH als Berechnungsverfahren <i>[Link zu Hintergrundinformationen \u201eBehandlung von Analysen mit \u2264-Zeichen]<\/i> anwendet.<\/p><\/div><\/div>"},{"title":"Bewertung von Spurenstoffen im Trinkwasser ","text":"<div id=\"bewertung\" class=\"accordion-body collapse in\"><div class=\"accordion-inner\"><p class=\"bodytext\">Die modernen analytischen Verfahren erm\u00f6glichen es zunehmend, geringste Spuren von Stoffen im Wasser mengenm\u00e4\u00dfig zu bestimmen, so dass die Anzahl der erfassbaren organischen Komponenten in der Wassermatrix zurzeit st\u00e4ndig steigt. <br><b>Grenzwerte der Trinkwasserverordnung<\/b><br>Etwas mehr als 50 Parameter sind in der Trinkwasserverordnung mit Grenzwerten belegt, wobei die Pflanzenschutzmittel und Biozidprodukt-Wirkstoffe nicht einzeln genannt, sondern summarisch aufgef\u00fchrt sind. Die bei der Analytik zu ber\u00fccksichtigenden Komponenten werden in der Regel mit den Aufsichtsbeh\u00f6rden abgestimmt und regelm\u00e4\u00dfig auf Aktualit\u00e4t \u00fcberpr\u00fcft. In der Summe resultieren so gemeinsam mit den Pflanzenschutzmitteln und von Wasserwerk zu Wasserwerk etwas unterschiedlich f\u00fcr etwa 100 bis 120 Parameter Trinkwassergrenzwerte.<br>Zu den Stoffen, f\u00fcr die es in der Trinkwasserverordnung keine Grenzwerte gibt, geh\u00f6ren verschiedene Umweltchemikalien und auch die Arzneistoffe. Sie gelangen produktionsbedingt oder durch Entsorgung und durch die bestimmungsgem\u00e4\u00dfe Anwendung in die Gew\u00e4sser. Auch ohne eine gesetzliche oder beh\u00f6rdliche Vorgabe werden bei der Wasserwerke Westfalen GmbH und den Beteiligungsgesellschaften derartige Stoffe bereits seit l\u00e4ngerem untersucht.<br><b>Vorsorgewerte, Leitwerte, gesundheitliche Orientierungswerte (GOW)<\/b> <br>In der Trinkwasserverordnung sind f\u00fcr viele der analysierten Spurenstoffe keine Grenzwerte zur Beurteilung der gesundheitlichen Relevanz vorhanden. In einigen F\u00e4llen k\u00f6nnen zur Bewertung aber Empfehlungen des Umweltbundesamtes (UBA) oder anderer Stellen herangezogen werden. F\u00fcr das Trinkwasser sind insbesondere die vom UBA aufgestellten allgemeinen Leit- oder Vorsorgewerte geeignet. Sie sind daher in den Analysetabellen zus\u00e4tzlich zu den Grenzwerten der Trinkwasserverordnung in der Spalte \u201eVorsorgewerte\u201c aufgef\u00fchrt. Bei Substanzen, die das UBA hinsichtlich der gesundheitlichen Relevanz bewertet hat, sind die GOW allein als Zahl angegeben. F\u00fcr Substanzen, die nicht oder bisher lediglich teilbewertet wurden, ist der allgemeine Vorsorgewert von 0,1 \u00b5g\/l&nbsp;mit einem f\u00fchrenden \"V\"&nbsp;angegeben. Trinkwasser Leitwerte hingegen sind mit dem K\u00fcrzel \"LW\" gekennzeichnet. Diese allgemeinen Vorsorge- und Leitwerte unterscheiden sich von den GOW lediglich in der Bewertungstiefe.<br>Informationen \u00fcber die unterschiedlichen Bewertungsans\u00e4tze sind beispielsweise unter&nbsp;<a href=\"https:\/\/www.umweltbundesamt.de\/dokument\/grenzwerte-leitwerte-orientierungswerte\" title=\"Opens external link in new window\" target=\"_blank\" class=\"external-link-new-window\">https:\/\/www.umweltbundesamt.de\/dokument\/grenzwerte-leitwerte-orientierungswerte<\/a> zu finden.<br><b>Parameter ohne Bewertungsspalte<\/b><br>Bei Stoffen, f\u00fcr die kein Trinkwassergrenzwert festgelegt ist und die gesundheitlich ohne Bedeutung sind, sind in den Bewertungsspalten keine Angaben enthalten.<\/p>\n<p style=\"padding-left: 10px; margin-top: 10px;\" class=\"bodytext\"> <span style=\"font-style: italic;\">Anmerkung:<\/span><br> \t\tDie gesundheitlichen Leitwerte basieren auf den lebenslangen Konsum von t\u00e4glich 2 Litern Wasser. Grundlage der Bewertung sind daher nicht die Maximalwerte, sondern die Durchschnittswerte \t\t(siehe \t\t<a href=\"http:\/\/www.umweltbundesamt.de\/sites\/default\/files\/medien\/374\/dokumente\/gow-empfehlung_2003_46.pdf\" target=\"_blank\">http:\/\/www.umweltbundesamt.de\/sites\/default\/files\/medien\/374\/dokumente\/gow-empfehlung_2003_46.pdf<\/a>).&nbsp;&nbsp;\t<\/p><\/div><\/div>"},{"title":" Darstellung von Summengrenzwerten ","text":"<div id=\"summengrenzwerte\" class=\"accordion-body collapse in\"><div class=\"accordion-inner\"><p class=\"bodytext\"> In der Trinkwasserverordnung aber auch bei den gesundheitlichen Vorsorgewerten sind in manchen F\u00e4llen Grenz- oder Leitwerte f\u00fcr mehrere Teilkomponenten oder f\u00fcr die Summe einer ganzen Stoffklasse formuliert. So gilt beispielsweise f\u00fcr die Summe aller analysierten Pflanzenschutzmittel und Biozidprodukte ein Trinkwassergrenzwert von 0,5 Mikrogramm pro Liter [\u00b5g\/l]. \n<\/p>\n<p class=\"bodytext\"> Bei Grenz- oder Leitwerten f\u00fcr die Summe mehrerer Parameter sind in der Spalte \u201eGrenzwert\u201c bzw. \u201eVorsorgewert\u201c diese maximal m\u00f6glichen Konzentrationen auch bei jedem der Teilparameter eingetragen, denn positive Ergebnisse d\u00fcrfen bis zu der genannten H\u00f6he vorkommen, wenn von den \u00fcbrigen Teilkomponenten sonst keiner nachweisbar ist. Zu beachten ist hier, dass zur Beurteilung der Analysen Teilparameter unter der Bestimmungsgrenze bei der Summenbildung nicht ber\u00fccksichtigt werden.<\/p><\/div><\/div>"},{"title":"Relevanz mikrobiologischer Parameter ","text":"<div id=\"relevanz\" class=\"accordion-body collapse in\"><div class=\"accordion-inner\"><p class=\"bodytext\">Entsprechend der Trinkwasserverordnung sind bei mikrobiologischen Parametern Kulturverfahren anzuwenden, bei denen die auf den speziellen N\u00e4hrmedien gewachsenen Kolonien gez\u00e4hlt werden. Ausgewertet werden diese als koloniebildende Einheiten (KBE).<br>Bei der Bewertung der Ergebnisse ist zu beachten, dass Mikroorganismen sich nicht gleichm\u00e4\u00dfig verteilt in L\u00f6sung befinden (wie die meisten chemischen Stoffe). So k\u00f6nnen sich von den Innenwandungen der Leitungen einzelne, kleine Flocken des \u00fcblicherweise vorhandenen d\u00fcnnen Biofilms abl\u00f6sen. H\u00f6here Werte bei den mikrobiologischen Parametern beruhen dann nicht selten darauf, dass eine einzelne kleine Flocke in die Probe gelangt und diese somit nicht repr\u00e4sentativ f\u00fcr die untersuchte Wasserqualit\u00e4t ist. Als weitere M\u00f6glichkeit muss immer auch gepr\u00fcft werden, ob nicht Vorg\u00e4nge im Umfeld der Probenahme und der Zapfstelle zu einer Verf\u00e4lschung des Ergebnisses gef\u00fchrt haben k\u00f6nnten.<br>Aus den genannten Gr\u00fcnden m\u00fcssen Einzelwerte bei mikrobiologischen Parametern im Regelfall durch Nachkontrollen bet\u00e4tigt werden. Weil damit die Maximalwerte (als Einzelwerte)&nbsp; im Allgemeinen nicht die abgegebene Trinkwasserqualit\u00e4t repr\u00e4sentieren werden bei der Gruppe der mikrobiologischen Parameter keine Minima und Maxima ausgegeben.<br><b>Koloniezahlen<\/b><br>Hohe Koloniezahlen in Wasserwerksproben liefern Hinweise darauf, dass bei der Aufbereitung die verwertbaren organischen Stoffe nicht ausreichend abgebaut wurden. Hohe Koloniezahlen im Netz deuten darauf hin, dass eine N\u00e4hrstoffquelle vorliegen k\u00f6nnte, bei der zu pr\u00fcfen ist, ob sie auf einem Eindringen von Fremdwasser oder Fremdstoffen von au\u00dfen (z. B. unzul\u00e4ssige Verbindungen oder mangelnde Sorgfalt bei Arbeiten im Netz) beruhen.<br><b>Coliforme Bakterien\/E. coli<\/b><br>Bei den Coliformen Bakterien, zu denen auch E. coli z\u00e4hlt, handelt es sich um viele unterschiedliche Bakterienarten. Ein Teil der Coliformenarten kann aus Warmbl\u00fcterf\u00e4kalien kommen und zudem in der Umwelt beheimatet sein, w\u00e4hrend ein anderer Teil&nbsp; ausschlie\u00dflich in der Umwelt vorkommt. Daher wird beim Nachweis von Coliformen Bakterien in R\u00fccksprache mit dem zust\u00e4ndigen Gesundheitsamt vorrangig eine Ursachenfindung angesto\u00dfen, um weitere Ma\u00dfnahmen abzuleiten. <br>Den h\u00f6chsten Indikatorwert hat E. coli. Das Bakterium ist in der Umwelt beschr\u00e4nkt lebensf\u00e4hig, als Ursprung stammt es aber immer aus einer F\u00e4kalbelastung von Warmbl\u00fctern oder dem Menschen, in deren Darm E. coli Bakterien enthalten sind. Der Trinkwassergrenzwert f\u00fcr Coliforme Bakterien und E. coli gilt f\u00fcr ein Probevolumen von 100 ml, die stets anzusetzen und zu untersuchen sind.<br><b>Enterokokken<\/b><br>Enterokokken haben denselben hohen Indikatorwert wie E. coli. Auch sie sind grunds\u00e4tzlich f\u00e4kalen Ursprungs. Da sie in der Umwelt im Allgemeinen l\u00e4nger \u00fcberdauern als E. coli k\u00f6nnen sie erg\u00e4nzend zu diesen etwas \u00fcber den Zeitraum des Eintritts in das Wasserversorgungssystem aussagen.<br><b>Clostridium perfringens<\/b><br>Clostridium perfringens ist 2001 in das Untersuchungskonzept der Trinkwasser\u00fcberwachung \u00fcbernommen worden. Den gew\u00fcnschten Indikatorwert hat hier nicht das Bakterium selbst, sondern seine Dauerstadien. Diese Sporen sind sehr widerstandsf\u00e4hig gegen die zul\u00e4ssigen chemischen Desinfektionsmittel. Die Untersuchung auf Clostridien soll sicherstellen, dass sich keine einzelligen tierischen Parasiten im Trinkwasser befinden. Zu nennen sind hier vor allem Cryptosporidium und Giardia, die bereits in geringer Anzahl Durchfallerkrankungen hervorrufen.<br>Da bei den Parasiten die Untersuchung von mehreren 100 Litern erforderlich ist, um eine eventuelle hygienische Relevanz auszuschlie\u00dfen, werden die Clostridien an ihrer Stelle als Indikatoren untersucht. Das ist m\u00f6glich, weil die Clostridiensporen eine vergleichbare Resistenz gegen\u00fcber chemischen Desinfektionsmitteln haben wie die der Parasiten. Vorteilhaft ist, dass die Clostridien in Oberfl\u00e4chenw\u00e4ssern im Allgemeinen in bestimmbaren Konzentrationen vorkommen und sie bei den Aufbereitungsschritten \u201edurchg\u00e4ngiger\u201c sind als Parasitensporen. Wenn Clostridium perfringens nicht nachweisbar ist, ist davon auszugehen, dass sich auch keine Parasiten im Trinkwasser befinden.<\/p><\/div><\/div>"},{"title":"Hinweise zu den Radioaktivit\u00e4tsparametern der Trinkwasserverordnung ","text":"<div id=\"radioaktiv\" class=\"accordion-body collapse in\"><div class=\"accordion-inner\"><p class=\"bodytext\">Nachdem bei den Diskussionen zur Novellierung der Trinkwasserverordnung die Vorgaben zu den Radioaktivit\u00e4tsparametern erarbeitet waren, hat die Wasserwerke Westfalen GmbH entsprechende Untersuchungen gem\u00e4\u00df dem damals vorliegenden Entwurf in Auftrag gegeben. Die Untersuchungen zu den Aktivit\u00e4ten von Radon-222, Gesamt-alpha und Gesamt-beta wurden bei dem f\u00fcr Radioaktivit\u00e4tsparameter akkreditierten Laboratorium IWW Rhein-Main durchgef\u00fchrt und die Proben nach den Vorgaben des Instituts entnommen. Die Probenahme entsprach den zu dieser Zeit geltenden anerkannten Regeln der Technik und unterscheidet sich nicht wesentlich gegen\u00fcber den aktuellen Vorgaben an die Beprobung.<br>Die Untersuchungen im Zeitraum 2009 bis 2012 best\u00e4tigen, dass die Vorgaben der geltenden Trinkwasserverordnung in der Fassung vom 28. November 2015 eingehalten werden. Es liegen somit repr\u00e4sentative Daten vor, die zeigen, dass die Richtwerte f\u00fcr Radon-222 und die Richtdosis f\u00fcr alle seinerzeit untersuchten Trinkw\u00e4sser eingehalten werden und die Erstuntersuchung somit entfallen k\u00f6nnten.<\/p><\/div><\/div>"},{"title":"Geruchsschwellenwert","text":"<p class=\"bodytext\">Die Trinkwasserverordnung sieht vor, das Trinkwasser im Zuge der Beprobungen routinem\u00e4\u00dfig sensorisch zu \u00fcberpr\u00fcfen. Sollte bei der vor-Ort-Kontrolle ein un\u00fcblicher Geruch auffallen, wird eine Probe zur weiteren Untersuchung in einen geruchsfreien Beh\u00e4lter abgef\u00fcllt und in einer geruchsneutralen Umgebung der Geruchsschwellenwert (GSW) bestimmt. Der Geruchsschwellenwert wird in bestimmten Abst\u00e4nden auch dann \u00fcberpr\u00fcft, wenn bei der routinem\u00e4\u00dfigen Untersuchung keine Auff\u00e4lligkeiten festzustellen sind.<br>An der GSW-Bestimmung beteiligen sich wenigstens 2 Personen. Sie sollten keinen \u00fcberm\u00e4\u00dfig guten Geruchssinn haben, m\u00fcssen aber intensiv geschult werden. Bei der Pr\u00fcfung wird die Probe in einem Gef\u00e4\u00df mit gro\u00dfer Wasserfl\u00e4che unmittelbar dem Geruchssinn zugef\u00fchrt, nachdem sie auf 23 \u00b0C erw\u00e4rmt wurde. Gepr\u00fcft wird dabei, ob sich die Probe geruchlich von einer neutralen Vergleichsprobe unterscheidet. Bei unterschiedlichen Bewertungen der beiden Pr\u00fcfer wird die Pr\u00fcfung wiederholt und ggf. eine dritte Person hinzugezogen. Proben, die unverd\u00fcnnt einen Geruch aufweisen, werden mit 23 \u00b0C warmem, geruchsfreiem Wasser verd\u00fcnnt, bis Probe und Vergleichswasser nicht mehr unterscheidbar sind. Ein eventueller Geruch nach Desinfektionsmitteln wird bei der Bewertung nicht ber\u00fccksichtigt.<br>Wenn eine Probe (unverd\u00fcnnt) geruchsfrei ist, hat sie einen Geruchsschwellenwert von 1. Da durch Auslaugungs-, L\u00f6se-, und elektrochemische Prozesse und durch die Aktivit\u00e4t von Organismen Rohw\u00e4sser h\u00e4ufig geruchsbildende Substanzen enthalten, ist es Aufgabe der Trinkwasseraufbereitung, diese weitest m\u00f6glich zu entfernen. Der Trinkwassergrenzwert f\u00fcr die Geruchsschwelle betr\u00e4gt 3. Es bedeutet, dass kein Geruch festgestellt werden kann, wenn die Ausgangsprobe mit der doppelten Menge an geruchsfreiem Wasser verd\u00fcnnt wurde. Der Wert ber\u00fccksichtigt, dass bereits geringste Spuren mancher Substanzen einen Geruch ausl\u00f6sen k\u00f6nnen und geruchsaktive Komponenten nicht immer vollst\u00e4ndig zu entfernen sind.<\/p>"},{"title":" Hinweise zu den Desinfektionsparametern","text":"<div id=\"umfang\" class=\"accordion-body collapse in\"><div class=\"accordion-inner\"><p class=\"bodytext\"> \tWenn zur Sicherstellung der Hygiene ein Wasser desinfiziert werden muss, gibt es in der Trinkwasserverordnung strikte Vorgaben nicht nur dazu, welche Verfahren angewendet werden, sondern auch dar\u00fcber, welche Mengen zum Einsatz kommen d\u00fcrfen. Bei der chemi-schen Desinfektion ist auch geregelt, dass trotz der nicht vermeidbaren Desinfektionsmittelzehrung Restgehalte nach Abschluss der Aufbereitung im Trinkwasser verbleiben und welche Menge als \u201e\u00dcberschuss\u201c bei der Abgabe ins Netz mindestens noch enthalten sein muss. Die Desinfektion ist somit eine Gr\u00f6\u00dfe, die in Abh\u00e4ngigkeit von der Rohwasserbeschaffenheit in einem komplexen Regelungssystem st\u00e4ndig im Hinblick auf die Vorgaben der Trinkwasserverordnung zu regulieren ist. \t \t \n<\/p>\n<p class=\"bodytext\"> \tDie Vorgaben zur Desinfektion sind in der beim Umweltbundesamt gef\u00fchrten Liste der \t\u201e<a href=\"http:\/\/www.umweltbundesamt.de\/sites\/default\/files\/medien\/481\/dokumente\/17_aenderung_aufbereitungsstoffe_desinfektionsverfahren_11_trinkwv_11_2012.pdf\" target=\"_blank\">Aufbereitungsstoffe und Desinfektionsverfahren<\/a>\u201c enthalten. \tDie auf \u00a7 11 der Trinkwasserverordnung basierende Liste wird st\u00e4ndig an neue Anforderungen angepasst. Gesetzlich bindend f\u00fcr die Wasserversorger ist die im \tBundesanzeiger des Ministeriums f\u00fcr Justiz ver\u00f6ffentlichte Version. Jegliche Verst\u00f6\u00dfe sind strafbewehrt. \tAktuell sind die Vorgaben der 17. \u00c4nderung der \u201e<a href=\"https:\/\/www.bundesanzeiger.de\/ebanzwww\/wexsservlet?page.navid=to_bookmark_official&amp;bookmark_id=8syN98tL9gF32P4nkOn\" target=\"_blank\">\u00a7-11-Liste<\/a>\u201c einzuhalten. \t\t \n<\/p>\n<p class=\"bodytext\"> \tDie wichtigsten chemischen Desinfektionsmittel sind Chlor (Cl2) und Chlordioxid (ClO2). Die maximal m\u00f6gliche Zugabe an Chlor ist auf 1,2 mg\/l begrenzt; \tdie von Chlordioxid auf 0,4 mg\/l. In Sonderf\u00e4llen d\u00fcrfen bis zu 6 mg\/l Chlor zugegeben werden. Falls es erforderlich ist, ein Wasser zu desinfizieren; \tm\u00fcssen nach Abschluss der Aufbereitung noch wenigstens 0,1 mg\/l freies Chlor nachweisbar sein (bei Desinfektion mit Chlordioxid sind es 0,05 mg\/l ClO2). \tIm Falle der Desinfektion m\u00fcssen entstehende Reaktionsprodukte beachtet und \u00fcberwacht werden und zwar Trihalogenmethane (\u201eTHM\u201c) bei der Desinfektion mit \tChlor und Chlorit bei der Desinfektion mit Chlordioxid. \t\t \n<\/p>\n<p class=\"bodytext\"> \tNeben der chemischen Desinfektion ist als Desinfektionsverfahren auch die Behandlung des Wassers mit UV-Strahlen zul\u00e4ssig. \tHierbei muss sichergestellt werden, dass eine Dosis von mindestens 400 Joule\/m2 auf das Wasser einwirkt. Das ist \u00fcber die \t Bestrahlungsst\u00e4rke der UV-Leuchten (in Abh\u00e4ngigkeit vom Wasserfluss und eventuell enthaltenen Tr\u00fcbstoffpartikeln) sicher zu stellen. \t\t \n<\/p>\n<p class=\"bodytext\"> \t\t\tDas Trinkwasser der Ruhrwasserwerke muss st\u00e4ndig desinfiziert werden. Bei Grundwasserwerken ist das nur in Ausnahmef\u00e4llen erforderlich. \t\t\tBis vor einigen Jahren wurden die Trinkw\u00e4sser aus der Ruhr \u00fcberwiegend mit Chlordioxid behandelt. \t\t\tDie typischerweise erforderlichen Zugaben schwanken in Abh\u00e4ngigkeit von der Rohwasserbeschaffenheit zwischen 0,12 und 0,18 mg\/l ClO2, die \t\t\t Restkonzentrationen nach Aufbereitung liegen bei 0,10 bis 0,14 mg\/l ClO2. \t\t\tIm Zuge der Modernisierung der Anlagen wird zunehmend die chemiefreie UV-Technologie zur Trinkwasserdesinfektion eingesetzt. \t\t \n<\/p>\n<p class=\"bodytext\"> \t\t\tDie Desinfektion wird, wie erl\u00e4utert, in einem automatisierten Regelprozess st\u00e4ndig an den jeweils aktuellen Bedarf angepasst und im Rahmen der gesetzlichen \t\t\tVorgaben variabel eingestellt. Aus diesem Grund haben die Werte der Labor\u00fcberwachung keine Aussagekraft zur Beurteilung der Trinkwasserbeschaffenheit. \t\t\tDie Messwerte der Desinfektionsparameter werden in den Datentabellen daher nicht dargestellt. \t\t<\/p><\/div><\/div>"}]},{"title":"FAQ","type":"foldList","entries":[{"title":"Warum ver\u00f6ffentlichen Sie diese Daten jetzt?","text":"<p class=\"bodytext\">Die Diskussionen \u00fcber Spurenstoffe haben deutlich gemacht, dass bei  unseren Kunden ein gro\u00dfes Interesse daran besteht zu erfahren, wie das  gelieferte Trinkwasser beschaffen ist. Die Wasserwerke Westfalen GmbH hat sich  darum entschlossen - \u00fcber die gesetzlichen Ver\u00f6ffentlichungspflichten  hinaus - die Erkenntnisse aus der immer feiner messenden Analytik  weiterzugeben. <\/p>"},{"title":"Warum sind Wasserwerke nicht in der Lage, auch kleinste Mengen Spurenstoffe zur\u00fcckzuhalten und damit ein reines Trinkwasser anzubieten?","text":"<p class=\"bodytext\">Die Trinkwasserversorgung in Deutschland ist auf ein m\u00f6glichst  naturbelassenes Trinkwasser ausgelegt. In der Trinkwasserverordnung sind  die Bedingungen festgelegt, wie Trinkwasser beschaffen sein muss.  Erg\u00e4nzende Orientierungswerte werden \u00fcber die Vorgaben der  Trinkwasserverordnung hinausgehend durch das Umweltbundesamt festgelegt.  Die Aufbereitungsanlagen der Wasserwerke sind dahingehend ausgelegt,  alle geltenden Werte sicher einzuhalten. Der Gesetzgeber pr\u00fcft und  \u00e4ndert ggf. die Grenz- oder Orientierungswerte sobald neue Kenntnisse  \u00fcber die Relevanz von Wasserinhaltsstoffen vorliegen. F\u00fcr einige Gruppen  von Spurenstoffen sind noch weitergehende Aufbereitungsschritte  grunds\u00e4tzlich technisch m\u00f6glich, aber angesichts der extrem geringen  Konzentrationen nicht mehr sinnvoll. Die Wasserwerke Westfalen GmbH setzt sich seit vielen  Jahrzehnten daf\u00fcr ein, eine weitere Reduzierung der Konzentrationen  durch vorbeugenden Gew\u00e4sserschutz zu erzielen, damit Trinkwasser auch  weiterhin ein Naturprodukt bleibt bzw. bleiben kann.<\/p>"},{"title":"Ist es gesundheitsgef\u00e4hrdend Ihr Leitungswasser zu trinken?","text":"<p class=\"bodytext\">Nein, das Trinkwasser ist hygienisch einwandfrei und toxikologisch  sicher und kann somit ohne Risiko uneingeschr\u00e4nkt im Haushalt und zum  Trinken verwendet werden.<\/p>"},{"title":"W\u00fcrden Sie mit Ihrem Leitungswasser Babynahrung zubereiten?","text":"<p class=\"bodytext\">Ja, es gibt keine Einschr\u00e4nkung in der Verwendung auch nicht bez\u00fcglich Babynahrung.<\/p>"},{"title":"Kann ich pers\u00f6nlich etwas tun, die Schadstoffmenge im Wasser weiter zu senken?","text":"<p class=\"bodytext\">Ja, achten Sie darauf, keine Schadstoffe in den Wasserkreislauf zu  leiten. Immer wieder werden zum Beispiel Medikamente \u00fcber die Toilette  entsorgt. Farben- oder Haushaltschemikalien geh\u00f6ren ebenso wenig ins  Abwasser.<\/p>"},{"title":"Ist es sinnvoll in zus\u00e4tzliche Hausaufbereitungsanlagen oder mobile Filter zu investieren?","text":"<p class=\"bodytext\">Nein, dazu besteht keinerlei Veranlassung. Das Trinkwasser ist hygienisch einwandfrei und toxikologisch sicher.<\/p>"},{"title":"Wie kommen diese Stoffe eigentlich ins Wasser?","text":"<p class=\"bodytext\">Die Eintragspfade sind vielf\u00e4ltig. Fl\u00fcsse zum Beispiel nehmen gekl\u00e4rtes  Abwasser aus kommunalen wie industriellen Kl\u00e4ranlagen auf. Zudem sind  Einleitungen von Gewerbebetrieben erlaubt. Aber auch  Starkregenereignisse schwemmen Schadstoffe von den Oberfl\u00e4chen der  St\u00e4dte wie von landwirtschaftlich genutzten Fl\u00e4chen ab. Im Grundwasser  finden sich Stoffe wie Nitrat und Abbauprodukte von  Pflanzenschutzmitteln wieder, h\u00e4ufig aus Anwendungen in der  Landwirtschaft.<\/p>"},{"title":"Es gibt auf der Welt tausende organische und anorganische Verbindungen. Nach welchen Kriterien suchen Sie aus, auf welche Stoffe Sie untersuchen?","text":"<p class=\"bodytext\">Mitarbeiter der Wasserwerke Westfalen GmbH wie der Westf\u00e4lischen Wasser- und Umweltanalytik GmbH (WWU)sind im st\u00e4ndigen Austausch \u00fcber die f\u00fcr das Wasser relevanten Stoffe. Ins Blickfeld gelangen dabei nicht nur die Ausgangsverbindungen, sondern auch deren Umwandlungsprodukte, die aus diesen Ausgangsstoffen in der Umwelt oder bei der Trinkwasseraufbereitung entstehen k\u00f6nnen und als \u201eMetabolite\" oder \u201eTransformationsprodukte\" bezeichnet werden. Von besonderer Bedeutung ist dabei die st\u00e4ndige fachliche Diskussion innerhalb der gesamten Wasserwirtschaft in Deutschland und Europa. Eingebunden in diesen Prozess sind sowohl die Unternehmen als auch die zust\u00e4ndigen Fachbeh\u00f6rden und die Fachverb\u00e4nde, wie z.B. der Deutsche Verein des Deutschen Gas- und Wasserfaches (DVGW).\n<\/p>\n<p class=\"bodytext\">Damit ist sichergestellt, dass auch neue Entwicklungen rechtzeitig erkannt werden. Sollten Stoffe f\u00fcr das Ruhr- oder Stevergebiet oder f\u00fcr das Rohwasser der Grundwasserwerke theoretisch oder praktisch als relevant eingestuft werden, gelangen sie ins langj\u00e4hrige Untersuchungsprogramm. Wenn im Zuge der \u00dcberwachung Stoffe vorkommen, f\u00fcr die es keine Bewertung gibt, fragt die Wasserwerke Westfalen GmbH aktiv beim Bundesumweltamt um eine Bewertung nach. Dies ist beispielsweise beim Stoff TOSU so geschehen.<\/p>"}]},{"title":"Links","type":"linkList","entries":[{"title":"http:\/\/www.umweltbundesamt.de\/themen\/wasser","url":"http:\/\/www.umweltbundesamt.de\/themen\/wasser"},{"title":"UBA-Brosch\u00fcren zum Thema Trinkwasser: Rund um das Trinkwasser","url":"https:\/\/www.umweltbundesamt.de\/publikationen\/ratgeber-trink-was-trinkwasser-aus-hahn"},{"title":"UBA-Brosch\u00fcren zum Thema Trinkwasser: Trinkwasser-Installationen","url":"https:\/\/www.umweltbundesamt.de\/sites\/default\/files\/medien\/479\/publikationen\/uba_rund_um_das_trinkwasser_ratgeber_web_0.pdf"},{"title":"http:\/\/www.bfr.bund.de\/de\/a-z_index\/trinkwasser-4677.html#fragment-2","url":"http:\/\/www.bfr.bund.de\/de\/a-z_index\/trinkwasser-4677.html#fragment-2"},{"title":"http:\/\/www.bvl.bund.de\/DE\/01_Lebensmittel\/03_Verbraucher\/15_Wasser_Mineralwasser\/wasser_node.html","url":"http:\/\/www.bvl.bund.de\/DE\/01_Lebensmittel\/03_Verbraucher\/15_Wasser_Mineralwasser\/wasser_node.html"},{"title":"http:\/\/www.umwelt.nrw.de\/umwelt\/wasser\/trinkwasser\/index.php","url":"https:\/\/www.umwelt.nrw.de\/umwelt\/umwelt-und-wasser\/wasserversorgung-und-trinkwasser\/"},{"title":"http:\/\/www.lanuv.nrw.de\/wasser\/versorger\/trinkwasser.htm","url":"https:\/\/www.lanuv.nrw.de\/umwelt\/wasser\/wasserversorgungtrinkwasser"},{"title":"http:\/\/www.dvgw.de\/wasser\/trinkwasser-und-gesundheit\/","url":"http:\/\/www.dvgw.de\/wasser\/trinkwasser-und-gesundheit\/"}]},{"title":"Abk\u00fcrzungen","type":"foldList","entries":[{"title":"PFT","text":"<p class=\"bodytext\"><b>P<\/b>er<b>f<\/b>luorierte <b>T<\/b>enside<br> \t\t\t\t\t\tWeitere Erkl\u00e4rung innerhalb der Analyse unter: Organische Spurenstoffe \u2192 Perfluorierte Verbindungen. \t\t\t\t\t\t<\/p>"},{"title":"pH-Wert","text":"<p class=\"bodytext\">Der <b>pH-Wert<\/b> ist ein Ma\u00df f\u00fcr den sauren oder basischen  (alkalischen) Charakter eines Trinkwassers. Er ist eine dimensionslose  Zahl und gibt die Wasserstoffionen-Konzentration im Wasser an.<br> \t\t\t\t\t \tEin Wasser ist neutral, wenn sein pH-Wert bei 7,0 liegt. Unter pH 7,0  ist ein Wasser sauer, \u00fcber pH 7,0 ist ein Wasser basisch.<br> \t\t\t\t\t\t Trinkwasserleitungen oder Armaturen k\u00f6nnen durch saures oder  ungepuffertes Wasser angegriffen werden. Daher ist es n\u00f6tig das  Trinkwasser in das Kalk-Kohlens\u00e4ure-Gleichgewicht zu bringen. Hierbei  spielen die H\u00e4rtebildner Calcium und Magnesium im Zusammenhang mit der  freien Kohlens\u00e4ure eine Rolle. Die Vorgabe der Trinkwasserverordnung  legt einen Bereich von pH \u2265 6,9 und \u2264 9,5 fest. Bei den meisten  Trinkw\u00e4ssern liegt der pH-Wert zwischen 7,3 und 8,1 und entspricht somit  der Forderung der Trinkwasserverordnung. \t\t\t\t\t\t<\/p>"},{"title":"PSM","text":"<p class=\"bodytext\"><b>P<\/b>flanzen<b>s<\/b>chutz<b>m<\/b>ittel<br> \t\t\t\t\t\tWeitere Erkl\u00e4rung  innerhalb der Analyse unter: Organische Spurenstoffe \u2192 Pflanzenschutz-  und Sch\u00e4dlingsbek\u00e4mpfungsmittel. \t\t\t\t\t\t<\/p>"},{"title":"SAK","text":"<p class=\"bodytext\"> \t\t\t\t\t\t<b>S<\/b>pektraler <b>A<\/b>bsorptions<b>k<\/b>oeffizient<br>  \t\t\t\t\t\tDer Spektrale Absorptionskoeffizient kann bei verschiedenen  Wellenl\u00e4ngen gemessen werden und ist ein Ma\u00df f\u00fcr die Durchl\u00e4ssigkeit des  Wassers von Licht.<br> \t\t\t\t\t\tBei einer Wellenl\u00e4nge von 254 nm  (Nanometer) absorbieren haupts\u00e4chlich organische Stoffe das Licht.  Dieser Parameter ist somit ein Summenparameter zur Beurteilung der  organischen Inhaltstoffe eines Trinkwassers.<br> \t\t\t\t\t\tBei einer Wellenl\u00e4nge von 436 nm (Nanometer) wird die F\u00e4rbung des Wassers gemessen.<\/p>"},{"title":"THM","text":"<p class=\"bodytext\"><b>T<\/b>ri<b>h<\/b>alogen<b>m<\/b>ethane<br> \t\t\t\t\t\tWeitere Erkl\u00e4rung innerhalb der Analyse unter: Organische Spurenstoffe \u2192 Trihalogenmethane. \t\t\t\t\t\t<\/p>"},{"title":"TOC\/DOC","text":"<p class=\"bodytext\"><b>T<\/b>otal <b>O<\/b>rganic <b>C<\/b>arbon (Gesamt organischer  Kohlenstoff) ist ein Summenparameter f\u00fcr alle organischen Bestandteile  im Wasser. Dabei handelt es sich haupts\u00e4chlich um nat\u00fcrliche  Verbindungen wie z.B. Huminstoffe.<br><br> \t\t\t\t\t\t<b>D<\/b>issolved <b>O<\/b>rganic <b>C<\/b>arbon (Gel\u00f6ster Organischer Kohlenstoff)<br>  \t\t\t\t\t\tDer Wert des DOC ist meistens identisch mit dem Wert des TOC, da  im Trinkwasser keine oder nur sehr geringe Anteile an ungel\u00f6sten Stoffen  vorhanden sind. \t\t\t\t\t\t<\/p>"},{"title":"ETBE","text":"<p class=\"bodytext\"><b>E<\/b>thyl-<b>t<\/b>erti\u00e4r-<b>b<\/b>utyl<b>e<\/b>sther<br> \t\t\t\t\t\t\tWeitere Erkl\u00e4rung innerhalb der Analyse unter: Organische Spurenstoffe \u2192 Leichtfl\u00fcchtige Kohlenwasserstoffe \t\t\t\t\t\t<\/p>"},{"title":"GOW","text":"<p class=\"bodytext\"><b>G<\/b>esundheitlicher <b>O<\/b>rientierungs<b>w<\/b>ert<br> \t\t\t\t\t\tWeitere Erkl\u00e4rung unter: Informationen \u2192 Bewertung von Spurenstoffen.<\/p>"},{"title":"LHKW","text":"<p class=\"bodytext\"><b>L<\/b>eichtfl\u00fcchtige <b>h<\/b>alogenierte <b>K<\/b>ohlen<b>w<\/b>asserstoffe<br> \t\t\t\t\t\tWeitere Erkl\u00e4rung innerhalb der Analyse unter: Organische Spurenstoffe \u2192 Leichtfl\u00fcchtige Kohlenwasserstoffe. \t\t\t\t\t\t<\/p>"},{"title":"MTBE","text":"<p class=\"bodytext\"><b>M<\/b>ethyl-<b>t<\/b>erti\u00e4r-<b>b<\/b>utylesther<br> \t\t\t\t\t\tWeitere Erkl\u00e4rung innerhalb der Analyse unter: Organische Spurenstoffe \u2192 Leichtfl\u00fcchtige Kohlenwasserstoffe \t\t\t\t\t\t<\/p>"},{"title":"PAK","text":"<p class=\"bodytext\"><b>P<\/b>olyzyklische <b>a<\/b>romatische <b>K<\/b>ohlenwasserstoffe<br> \t\t\t\t\t\tWeitere Erkl\u00e4rung innerhalb der Analyse unter: Organische Spurenstoffe \u2192 Polyzyklische aromatische Kohlenwasserstoffe.<\/p>"}]},{"title":"Downloads"}]},"orte":[{"id":"60201","ort":"Ahlen"},{"id":"60202","ort":"Arnsberg"},{"id":"60203","ort":"Ascheberg"},{"id":"60204","ort":"Bad 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Eine akute Gef\u00e4hrdung ist dadurch nicht zu bef\u00fcrchten. 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