v1-v7 םוגידל היצדילו חוד 18/10/2015 · i םיניינע ןכות í ........
TRANSCRIPT
V1-V7 ח ולידציה לדיגום"דו
18/10/2015
i
תוכן עניינים
1 ........................................................................................................................................................ מנהלי סיכום
1 .................................................................................................................................... וניטור האתר פעילות
1 ........................................................................................................................................................ חריגות
2 ...................................................................................................................................................... הקדמה 1.0
3 ........................................................................................................ באתר הלוטים של עדכני וסטטוס מיקום 2.0
3.0 V1 – 5 .................................................................................................. הנחל במי המרחפים המוצקים כל סך
4.0 V2 – 6 .............................................................................................................. לנחל השחרור לפני השפך מי
6 ........................................................................................................................ (TSS) מרחפים מוצקים כ"סה
6 ........................................................................................................................................... (TN) כללי חנקן
6 ........................................................................................................................................... אמוניאקלי חנקן
TM ........................................................................................................................................ 7)) כללי מתכות
5.0 L3 – 8 .............................................................................................. בצנטרפוגות סחיטה לאחר גולמי סדימנט
L3 ................................................................................................................................................... 10 סיכום
6.0 L4 – 11 ....................................................................................... ביורמידיאציה לפני ערבוב לאחר סדימנט
L4 ................................................................................................................................................... 15 סיכום
7.0 L5– 16 .................................................................................... ביורמידיאציה במהלך ערבוב לאחר סדימנט
L5 ................................................................................................................................................... 16 סיכום
8.0 L6– 17 .................................................................................................. ביורמידיאציה לאחר מעורבב סדימנט
18 .......................................................................................................................................... יתסופ ולידציה 9.0
10.0 V7 - 19 ..................................................................................................................... חודשי אויר איכות ניטור
20 .............................................................................................................................. חריגים ניטור מאורעות 11.0
21 ...................................................................................................................................... האתר מפרט – 1 נספח
JONES ENVIRONMENTAL LABORATORY ................................................... 26 ממעבדת ולידציה חות"דו – 2 נפסח
רשימת טבלאות
1 ................................................................................................................... וניטור אתר פעילות סיכום: 1.01 טבלה
3 ......................................................................................................... באתר ים'הבאצ של עדכני סיכום: 2.01 טבלה
4 ............................................................................................ באתר ים'הבאצ ולידציית של עדכני סיכום: 2.02 טבלה
6 ............................................................................. (mg/l) השפך ערכי –( TSS) מרחפים מוצקים כ"סה: 4.01 טבלה
6 .......................................................... (mg/l) השפך ערכי סטטיסטיקת –( TSS) מרחפים מוצקים כ"סה: 4.02 טבלה
6 ................................................................................................................... (mg/l) השפך ערכי – TN: 4.03 טבלה
6 ................................................................................................ (mg/l) השפך ערכי סטטיסטיקת – TN: 4.04 טבלה
6 ................................................................................................................ (mg/l) השפך ערכי – NH3 :4.05 טבלה
6 .............................................................................................. (mg/l) השפך ערכי סטטיסטיקת – NH3: 4.06 טבלה
7 ................................................................................................................... (mg/l) השפך ערכי – TM: 4.07 טבלה
7 ................................................................................................(mg/l) השפך ערכי סטטיסטיקת – TM: 4.08 טבלה
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
ii 18/10/2015 רשות ניקוז ונחלים קישון
7 ...............................................................................................................................השפך ערכי – pH: 4.09 טבלה
8 ......................................................................................................... (S229-ו S228 וטל) מפורט TPH: 5.01 טבלה
8 ............................................................................................................ (S229-ו S228 וטל) כללי TPH: 5.02 טבלה
8 ........................................................................................................ (S229-ו S228 וטל) לחות ולתתכ: 5.03 טבלה
9 ................................................................................................................ (S229-ו S228 וטל) PAH’s: 5.04 טבלה
9 ............................................................................................................... (S229-ו S228 וטל) SVOC’s: 5.05 טבלה
10 .............................................................................. (S229-ו S228 וטל) PHENOLS & PHTHALATES : 5.06 טבלה
10 ........................................................................................................................... כללי מתכות -TM : 5.07 טבלה
11 .............................................................. (SP209 - ו SP225, SP228, SP227,SP226 יםלוט) כללי TPH: 6.02 טבלה
TM ................................................................................................................................................. 15: 6.09 טבלה
15 ......................................................................................................... תשטיפים – Leachable Metals:6.10 טבלה
16 ................................................................................................................ (SP166 לוט) מפורט TPH: 7.01 טבלה
16 .................................................................................................................... (SP166 לוט) כללי TPH: 7.02 טבלה
16 ................................................................................................................ (SP166 לוט) לחות תכולת: 7.03 טבלה
18 ........................................................ (SP228 -ו SP209 ,SP225,SP226,SP227 לוטים) סופית ולידציה: 9.01 טבלה
רשימת איורים
22 ........................................................................................................................................ ולידציה סכמת: 1 איור
23 ............................................................................................................................... הראשי האתר מפרט: 2 יורא
L4 ....................................................................................................................................... 24 - ו L3 מיקום: 3 איור
25 ........................................................................................................... (Windrows) הטיפול שורות מיקום: 4 איור
פרוייקט חפירה וטיפול סדימנט נחל הקישון בועידוח ניטור ש
18/10/2015 1 רשות ניקוז ונחלים קישון
ום מנהלי סיכ
פעילות האתר וניטור 4/10/15 –פעילות האתר והניטור השבועית מסוכמת בטבלה המוצגת מטה, עבור התקופה בין ה
מסכמת את הפעילות היומית באתר כולל חפירה, שחרור מים 1.01. טבלה 17/10/2015 –עד ל
עולות הניטור ( ופעילות הצנטרפוגות )סחיטת בוצה(. בנוסף הטבלה מציגה את פLPPלנחל )
שהתבצעו על פי ימים בהתאם לפעילות האתר.
ח זה. "וסבר בדובאתר לניטור המבוצע ברמה היומית תכל אי התאמה בין הפעילות
וניטור אתר פעילות סיכום: 1.01 טבלה
. הדיגום 12/12/2014אינו מתרחש ברמה היומית מאז ( L3) לאחר סחיטה גולמי דיגום סדימנט
עקב תפוקה יומית נמוכה נדרשים מספר ימים להשלמת באצ' אצווה )באצ'( שלמה.נעשה עבור כל
L3. דיגום 1000m3)בממוצע כיומיים מלאים של פעילות חפירה(. נפח באצ' בודד אינו עולה מעל
לשלב העירבוב. תהקודם לערבוב, מתרחש כאשר באר מלאה )באצ' שלם( עובר
שעות ביממה, אלא אם ישנה חריגה 24שוטף של אספקת מי המיהול מבזן מאפשרים שחרור
מועברת לסחרור על מנת להגן על הביומסה כשאר אין חפירה מספר LPP-שבריכת האו בפרמטרים
הייתה LPP-רק במידה ובריכת ה .בפעילות החפירה יותר על כן השחרור אינו תלויימים רצופים,
ר לנחל. בסחרור כתוצאה מאי חפירה מתמשכת לא ייתרחש שחרו
(. בתוכנית העבודה בדרישות המכרז )וילונות כפולים הותקנו בנחל וילונות העומדים 22/6/2015 –ב
לא היו מותקנים וילונות העומדים 22/6/2015 –אמור להתבצע ברמה השבועית, עד ל V1דיגום
משיך התבצע ברמה יומית. לאחר התקנת הוילונות הדיגום ה V1בדרישת המכרז ועל כן דיגום
–להתבצע ברמה יומית על מנת לוודא כי אכן אין חריגות ברמת המוצקים המרחפים בנחל. החל מה
. יתבצע ברמה שבועית בהתאם לדרישת המכרז ותוכנית העבודה V1דיגום 5/7/2015
חריגות
3L – "בערכי תה חריגה אחתוהזח במהלך תקופת הדוTPH .
L4 – בערכי זוהו חריגותלא במהלך תקופת הדו"חTPH.
L5 – בערכי חריגות שתי זוהובמהלך תקופת הדו"חTPH.
Start EndDredger
Operation (V1)
LPP
Discharge
(V2)
Centrifuge
Operation (L3)V1 V2 L3
4/10/2015 No Yes Yes No No Yes
5/10/2015 No No No No No No
6/10/2015 No No No No No No
7/10/2015 No No No No No No
8/10/2015 No No No No No No
9/10/2015 No No No No No No
11/10/2015 No No No No No No
12/10/2015 No No No No No No
13/10/2015 No No No No No No
14/10/2015 No No No No No No
15/10/2015 No No No No No Yes
16/10/2015 No No No No No No
17/10/2015 No No No No No No
TOTAL DAYS 0 1 1 0 0 2
Date
Site Activities Validation TestingDredging Time
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 2 וןרשות ניקוז ונחלים קיש
V1-V7 דוח ולידציה לדיגום
הקדמה 1.0
.17/10/2015 - 4/10/2015דוח זה מסכם את תוצאות הולידציה סדימנט ומים עבור התקופה
פה זו היא . מטרת פעילות האתר במהלך תקוK3789 – K3781טווח הדגימות בדוח מצויות ב
.A2 –ו A1 קרקע שמקורה בבריכותו ביורמדיאציה של הסדימנט הנחפר מקרקעית נחל הקישון
הדיגום נעשה במספר אתרים הן בתוך האתר והן במספר נקודות בנחל עצמו. את מיקום נקודות
תוצאות הדיגום מוצגות בטבלאות, כאשר .1בנספח אזור הטיפול בקרקע ניתן לראות והדיגום
במידה וישנן חריגות הן מצויינות, במידה וננקטו אמצעים להתמודדות עם החריגות יופיע תיאור
שלהם.
בטבלאות, חריגות מודגשות באדום בעוד שנתונים העומדים בתקנים מופיעים בירוק. במידה ומזוהה
חריגה בממוצע אך לא בערכים המקסימאליים, זו תופיע בכתום.
ם לשיטות המוצהרות. דיגום הולידציה שהתבצע המהלך תקופת הו"ח כל הדיגום נעשה בהתא
מפורט מטה:
L3 – סדימנט גולמי לאחר סחיטה בצנטרפוגות;
4L – ( לפני ביורמידיאציה חול –גזם ואנאורגני –סדימנט לאחר ערבוב )תוספת של חומר אורגני;
L5 – סדימנט לאחר ערבוב במהלך ביורמידיאציה;
V7 – איכות אויר חודשי ניטור
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 3 וןרשות ניקוז ונחלים קיש
מיקום וסטטוס עדכני של הלוטים באתר 0.0
מסכמת את הסטטוס של באצ'ים של קרקע המצויים באתר נכון לעת הגשת ד"ח זה, 2.01טבלה
הם באצ'ים יעודיים עבור S3-ו S2באצ'ים שלב הדחיסה. עד להחל משלב הסחיטה, שלב הטיפול ו
באצ'ים הם של סדימנט בשלבים שונים. , כל יתר הV2-ו V1דגימות
באתר ים'הבאצ של עדכני סיכום :2.01 טבלה
לא מצטבר חול, החול שנוצר נצרך ישירות לערבוב לתוך הסדימנט. 1/3/2015-מאז ה
אל אזור דחיסת הגבהות לאחר שעבר ומוזג SP228-וS218,SP221,SP222,,SP223 S227 יםבאצ'
ולידציה מלאה.
Lot/Batch Location StatusEstimated
Quantity - m3
Number
of
Samples
Notes
S2 Reports Only Varying Data N/A 2276 V1 TSS Data
S3 Reports Only Varying Data N/A 794 V2 Efflluent Data
S58
Test Pads-
Landscape /
Storage Area
Below Validation
Thresholds154953 534
Contains S1,S4,S5,S6,S7,S8,S9,S10,S11,S12,S13,
S14,S15,S16,S17,S19,S20,S21,S22,S24,S25,S26,S27,S29,S30,S31,S32,S33,S34,S35,S36,
S37,S38,S39,S40,S41,S42,S43,S44,S45,S46,S47,S49,S50,S51,S52,S53,S54,S55,S56,S57,
S59,S60,S61,S62,S63,S64,S65,S66,S67,S68,S69,S70,S71,S72,S73,S74,S75,S76,S77,S78,
S79,S80,S81,S82,S83,S84,S85,S86,S87,S88,S89,S90,S91,S93,S94,S95,S96,S97,S98,S99,
S100,S101,S102,S103,S104,S105,S106,S107,S108,S109,S110,S111,S112,S113,S114,S11
5,S116,S117,S118,S119,S120,S121,S122,S123,S124,S125,S126,S127,S128,S129,S130,S
131,S132,S133,S134,S135,S137,S138,SP139,SP140,SP141,SP142,SP143,SP144,SP145,S
146,S148,SP151,SP152,SP153,SP154,SP155,SP156,S157,S158,SP159,SP160,SP161,SP1
62,SP163,SP164,S165,SP171,SP172,SP173,S174,SP177,SP178,SP179,SP180,SP181,
S182,SP183,S184,SP185,
S186,S187,S188,S189,S190,SP191,SP192,SP193,SP194,SP195,SP196,S197,SP198,
SP199,SP200,S201,SP202,SP204,S205,S207,SP212,SP213,SP214,SP215,SP216,SP217,S
218,SP219,SP221,S222,SP223,S227 and SP228
S92 22 River Core Samples
SP147 PAD 2Above Validation
Thresholds3248 11 S136, S150 and S170
SP166 PAD 6Above Validation
Thresholds915 8 S208 (300 m3)
SP167 PAD 6Above Validation
Thresholds1150 3
SP168 PAD 5Above Validation
Thresholds1020 5
SP169 PAD 4Above Validation
Thresholds640 6 S182 (220m3)
SP206 PAD 3Below Validation
Thresholds1120 1
SP209 PAD 2Below Validation
Thresholds1800 1
SP211 PAD 4Below Validation
Thresholds1020 1
SP225 PAD 3Below Validation
Thresholds900 1
S229 PAD 1Below Validation
Thresholds3000 1
ייקט חפירה וטיפול סדימנט נחל הקישוןפרו דוח ניטור שבועי
18/10/2015 4 רשות ניקוז נחלים קישון
באתר ים'הבאצ ולידציית של עדכני סיכום :2.02 טבלה
Lot/Batch Relevant K-numberFinal Validation
Sample IDNotes
S58
2,K16,K25,K30,K35,K40,K47,K68,K76,K82,K93,K114,K115,K121,K132,K153,K169,K175,K186,K192,K208,K219,K225,K241,K242,K248,K249,K269,
K286,K297,K298,K299,K320,K331,K342,K343,K354,K365,K366,K367,K388,K399,K400,K401,K412,K434,K435,K436,K447,K448,K459,K470,K482,
K483,K484,K495,K506,K527,K528,K529,K540,K541,K542,K543,K544,K545,K561,K562,K578,K579,K580,K581,K582,K583,K614,K615,K616,K632,
K633,K634,K635,K651,K652,K653,K669,K670,K671,K688,K689,K690,K706,K707,K708,K709,K710,K711,K712,K743,K744,K745,K746,K762,K763,
K764,K766,K767,K771,K772,K773,K774,K775,K776,K777,K793,K795,K811,K812,K828,K829,K845,K846,K862,K863,K879,K880,K881,K882,K898,
K914,K930,K946,K947,K948,K964,K965,K981,K997,K1014,K1048,K1064,K1013,K1015,K1046,K1047,K1080,K1106,K1132,K1133,K1159,K1160,K
1180,K1181,K1193,K1194,K1202,K1213,K1267,K1268,K1231,K1232,K1250,K1251,K1286,K1287,K1309,K1310,K1326,K1327,K1345,K1346,K134
7,K1348,K1367,K1368,K1387,K1386,K1405,K1406,K1424,K1442,K1443,K1444,K1462,K1476,K1477,K1483,K1489,K1490,K1491,K1522,K1538,K
1539,K1540,K1551,K1558,K1559,K1575,K1576,K1592,K1598,K1599,K1600,K1601,K1607,K1623,K1624,K1625,K1641,K1657,K1658,K1664,K166
5,K1666,K1682,K1683,K1684,K1685,K1701,K1707,K1723,K1739,K1740,K1741,K1742,K1758,K1759,K1760,K1761,K1762,K1778,K1779,K1785,K
1786,K1802,K1803,K1804,K1805,K1806,K1807,K1818,K1819,K1820,K1821,K1822,K1823,K1824,K1835,K1841,K1842,K1858,K1859,K1860,K187
8,K1895,K1896,K1897,K1903,K1904,K1905,K1906,K1917,K1918,K1939,K1940,K1941,K1942,K1953,K1954,K1955,K1961,K1962,K1963,K1969,K
1970,K1971,K1972,K1988,K1989,K2005,K2006,K2007,K2023,K2024,K2040,K2041,K2072,K2073,K2074,K2075,K2081,K2097,K2113,K2114,K211
5,K2141,K2142,K2143,K2149,K2165,K2166,K2167,K2183,K2189,K2190,K2191,K2192,K2208,K2209,K2210,K2211,K2212,K2213,K2229,K2230,K
2231,K2262,K2263,K2274,K2275,K2287,K2301,K2302,K2323,K2324,K2325,K2336,K2337,K2348,K2359,K2360,K2361,K2362,K2390,K2421,K242
2,K2423,K2434,K2465,K2502,K2503,K2514,K2567,K2589,K2590,K2616,K2637,K2638,K2639,K2670,K2671,K2692,K2693,K2714,K2725,K2726,K
2742,K2743,K2764,K2765,K2766,K2767,K2778,K2789,K2800,K2821,K2822,K2833,K2844,K2865,K2867,K2887,K2898,K2909,K2920,K2931,K293
7,K2938,K2949,K2960,K2961,K2962,K2963,K2964,K2975,K2986,K2987,K3018,K3019,K3030,K3041,K3042,K3043,K3044,K3065,K3066,K3077,K
3088,K3089,K3100,K3100,K3101,K3102,K3103,K3114,K3141,K3152,K3163,K3163,K3185,K3186,K3187,K3188,K3189,K3190,K3201,K3211,K322
3,K3266,K3267,K3268,K3276,K3289,K3290,K3291,K3292,K3293,K3294,K3295,K3297,K3323,K3335,K3336,K3337,K3359,K3370,K3371,K3372,K
3388,K3389,K3390,K3391,K3392,K3404,K3405,K3406,K3408,K3419,K3430,K3403,K3407,K3431,K3432,K3434,K3435,K3436,K3437,K3453,K345
4,K3455,K3456,K3458,K3459,K3461,K3462,K3463,K3464,K3465,K3466,K3467,K3478,K3479,K3494,K3495K3496,K3529,K3542,K3543,K3544,K3
559,K3562,K3577,K3578,K3579,K3580,K3581,K3582,K3583,K3584,K3585,K3586,K3587,K3589,K3601,K3602,K3603,K3604,K3605,K3606,K3626
,K3702,K3717,K3718,K3729,K3730,K3731,K3732,K3733,K3734,K3735,K3736,K3752,K3753,K3780,K3781,K3782,K3783,K3786
K35,K47,K115,K169,K186,K208,K242,K297,K298,K29
9,K366,K367,K401,K434,K448,K481,K482,K483,K543,
K544,K632,K669,K706,K709,K746,K812,K829,K846,K
863,K880,K881,K882,K947,K948,K965,K1013,K1014,
K1046,K1106,K1133,K1160,K1194,K1232,K1250,K12
67,K1287,K1327,K1346,K1347,K1387,K1406,K1442,K
1444,K1477,K1483,K1490,K1538,K1558,K1601,K162
4,K1658,K1664,K1665,K1683,K1742,K1786,K1807,K1
818,K1841,K1842,K1895,K1939,K1940,K1963,K1969,
K1970,K2006,K2041,K2081,K2141,K2166,K2190,K21
91,K2209,K2213,K2263,K2274,K2301,K2302,K2323,K
2325,K2360,K2390,K2421,K2423,K2434,K2502,K251
4,K2589,K2590,K2637,K2639,K2671,K2693,K2726,K2
743,K2766,K2778,K2789,K2822,K2833,K2865,K2887,
K2909,K2960,K2962,K2963,K2986,K3018,K3019,K30
41,K3043,K3064,K3077,K3089,K3101,K3103,K3141,K
3163,K3189,K3276,K3290,K3291,K3293,K3294,K329
5,K3335,K3336,K3359,K3370,K3372,K3389,K3390,K3
391,K3404,K3406,K3434,K3435,K3437,K3453,K3458,
K3459,K3461,K3462,K3463,K3464,K3465,K3466,K34
67,K3544,K3494,K3495,K3496,K3543,K3544,K3577,K
3578,K3580,K3581,K3582,K3584,K3585,K3589,K360
1,K3602,K3603,K3604,K3605,K3606,K3626,K3718,K3
729,K3730,K3731,K3732,K3733,K3734,K3735,K3736,
K3753,K3782,K3783,K3786
ContainsS1,S4,S5,S6,S7,S8,S9,S10,S11,S12,
S13,S14,S15,S16,S17,S19,S20,S21,S22,S24,S25,S26,
S27,S29,S30,S31,S32,S33,S34,S35,S36,S37,S38,S39,
S40,S41,S42,S43,S44,S45,S46,S47,S49,S50,S51,S52,
S53,S54,S55,S56,S57,S59,S60,S61,S62,S63,S64,S65,
S66,S67,S68,S69,S70,S71,S72,S73,S74,S75,S76,S77,
S78,S79,S80,S81,S82,S83,S84,S85,S86,S87,S88,S89,
S90,S91,S93,S94,S95,S96,S97,S98,S99,S100,S101,S1
02,S103,S104,S105,S106,S107,S108,S109,S110,S11
1,S112,S113,S114,S115,S116,S117,S118,S119,S120,
S121,S122,S123,S124,S125,S126,S127,S128,S129,S
130,S131,S132,S133,S134,S135,S137,S138,SP139,S
P140,SP141,SP142,SP143,SP144,SP145,S146,SP148
,SP151,SP152,SP153,SP154,SP155,SP156,S157,S158
,SP159,SP160,SP161,SP162,SP163,SP164,S165,SP17
1,SP172,SP173,SP174,SP175,SP176,SP177,S178,SP1
79,SP182,SP183,S184,SP185,S186,S187,S188
,S189,S190,SP191,SP192,SP193,SP194,SP195,S196,
S197,SP198,SP199,SP200,S201,SP202,SP203,SP204,
S205,SP207,S208,S210,SP212,SP213,SP214,SP215,S
P216,SP217,SP218,S219,SP220,SP221,SP222,SP223
,S224,S226,SP227 and SP228
S92 K2288-K2300 River Core Samples.
SP147 K3234,K3235,K3358,K3334,K3433,K3492,K3493,K3530,K3531,K3560,K3561 S136, S150,S170
SP166 K3480,K3545,K3563,K3614,K3628,K3629,K3630,K3631,K3703,K3704,K3705,K3706,K3754,K3755,K3784,K3785 S208 (300 m3)
SP167 K3481,K3456,K3564
SP168 K3460,K3527,K3557,K3566,K3612
SP169 K3436,K3457,K3528,K3558,K3565,K3613 S182
SP206 K3588
SP209 K3788
SP211 K3625 S224 S226
SP225 K3787 S226
S229 K3789
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 5 רשות ניקוז נחלים קישון
0.0 V1 – סך כל המוצקים המרחפים במי הנחל
בנחל. TSSת ובדיק התבצעה חפירה ממושכתולכן לא התבצעו בתקופת הדו"ח לא
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 6 רשות ניקוז נחלים קישון
0.0 V2 – מי השפך לפני השחרור לנחל
צטבר על הערכים הממוצעים . דו"ח זה מציג מידע מV2נלקחה דוגמת לא במהלך תקופת דו"ח זה
שנלקחו מתחילת הפרוייקט. V2 –והמקסימאליים של דוגמאות ה
(TSSמוצקים מרחפים )סה"כ
(mg/l) השפך ערכי –( TSS) מרחפים מוצקים כ"סה: 4.01 טבלה
(mg/l) השפך ערכי סטטיסטיקת –( TSS) מרחפים מוצקים כ"סה : 4.02 טבלה
(TNחנקן כללי )
(mg/l) השפך ערכי – TN: 4.03 טבלה
(mg/l) השפך ערכי סטטיסטיקת – TN :4.04 טבלה
חנקן אמוניאקלי
(mg/l) השפך ערכי – NH3 :4.05 טבלה
(mg/l) השפך ערכי סטטיסטיקת – NH3: 4.06 טבלה
Parameter MaximumDate
MaximumMinimum
Date
MinimumAverage Threshold
TSS 313 31/03/2014 10 27/12/2014 68.38 200
Parameter MaximumDate
MaximumMinimum
Date
MinimumAverage Threshold
TN 29.6 28/10/2014 3.4 16/11/2014 15.81 20
Parameter MaximumDate
MaximumMinimum
Date
MinimumAverage Threshold
Amm. N 17.14 29/07/2014 0.23 26/10/2014 2.82 5
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 7 רשות ניקוז נחלים קישון
TM)מתכות כללי ) (mg/l) השפך ערכי – TM: 4.07 טבלה
(mg/l) השפך רכיע סטטיסטיקת – TM: 4.08 טבלה
NB - Please note the numbers above are calculated by taking any result indicated as being <limit of detection (LOD) as the actual result, implying the maximum, minimum and average values or conservatively high, and in reality may
well be below the values indicated above.
(pHערך הגבה )
השפך ערכי – pH: 4.09 טבלה
Parameter Maximum Minimum AverageTotal Antimony 0.00700 0.00200 0.00214
Total Arsenic 0.02560 0.00250 0.00426
Total Beryllium 0.00060 0.00050 0.00047
Total Cadmium 0.00150 0.00050 0.00049
Total Chromium 0.01730 0.00150 0.00264
Total Cobalt 0.00500 0.00200 0.00193
Total Copper 0.00800 0.00700 0.00662
Total Lead 0.01800 0.00500 0.00503
Total Manganese 0.69200 0.01500 0.14504
Total Nickel 0.02600 0.00200 0.00303
Total Selenium 0.04500 0.00300 0.01389
Total Thallium 0.00400 0.00300 0.00284
Total Vanadium 0.03410 0.00150 0.00611
Total Zinc 1.01800 0.01000 0.12703
Mercury Total by CVAF 0.00005 0.00001 0.00001
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 8 רשות ניקוז נחלים קישון
5.0 L3 – סדימנט גולמי לאחר סחיטה בצנטרפוגות
מוצגות מטה. התוצאות S229 -ו S228 ים'עבור באצ L3 ותאדוגמ 2ו הלך תקופת הדו"ח נאספבמ
(S229-ו S228וט ל) מפורט TPH: 5.01 טבלה
(S229-ו S228וט ל) כללי TPH: 5.02 בלהט
(S229-ו S228וט ל) לחות תכולת: 5.03 טבלה
Sample ID Description Sampled Date >C5-C6 >C6-C8 >C8-C10 >C10-C12 >C12-
C16
>C16-
C21 >C21-C35 >C35-C44 Total
K3781 Cake 10/04/2015 <0.1 0.6 5.6 197.9 570 446 1087 178 2485
K3789 Cake 15/10/2015 <0.1 <0.1 1.3 9 31 32 76 11 160
Aliphatics (mg/kg)
Sample ID Description Sampled Date >EC5-EC7 >EC7-EC8 >EC8-EC10 >EC10-EC12 >EC12-
EC16
>EC16-
EC21
>EC21-
EC35
>EC35-
EC44Total
K3781 Cake 10/04/2015 <0.1 <0.1 0.6 <0.2 33 137 564 77 812
K3789 Cake 15/10/2015 <0.1 <0.1 <0.1 <0.2 <4 <7 34 <7 34
Aromatics (mg/kg)
Sample ID Lot/ Batch DescriptionTotal aliphatics and
aromatics (C5-44)Threshold
K3781 S228 Cake 3297 1,560
K3789 S229 Cake 194 1,560
TOTAL TPH (mg/kg)
Sample ID Lot/ Batch Description Moisture Content %
K3781 S228 Cake 66.3
K3789 S229 Cake 28.7
Moisture Content %
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 9 רשות ניקוז נחלים קישון
(S229-ו S228וט ל) PAH’s: 5.04 טבלה
(S229-ו S228וט ל) SVOC’s: 5.05 טבלה
Sample ID K3781 K3789
Lot/ Batch S228 S229
Description Cake Cake
Date 10/04/2015 15/10/2015
2-Chloronaphthalene <0.01 <0.01 681,000
2-Methylnaphthalene 0.13 <0.01 34,100
Naphthalene <0.01 <0.01 2.34
Acenaphthylene <0.01 <0.01 235,000
Acenaphthene <0.01 <0.01 223,000
Fluorene 0.03 <0.01 149,000
Phenanthrene 0.14 0.02 117,000
Anthracene <0.01 <0.01 1,120,000
Fluoranthene <0.01 <0.01 149,000
Pyrene 0.04 0.02 112,000
Benzo(a)anthracene <0.01 <0.01 350
Chrysene <0.01 <0.01 35,700
Benzo(bk)fluoranthene <0.01 <0.01 357
Benzo(a)pyrene <0.01 <0.01 36
Indeno(123cd)pyrene <0.01 <0.01 357
Dibenzo(ah)anthracene <0.01 <0.01 36
Benzo(ghi)perylene <0.01 <0.01 117,000
PAH's (mg/kg)
Threshold
Sample ID K3781 K3789
Lot/ Batch S228 S229
Description Cake Cake
Date 10/04/2015 15/10/2015
1,2-Dichlorobenzene <0.01 <0.01 303
1,2,4-Trichlorobenzene <0.01 <0.01 881
1,3-Dichlorobenzene <0.01 <0.01 4,300
1,4-Dichlorobenzene <0.01 <0.01 584
2-Nitroaniline <0.01 <0.01 5.35
2,4-Dinitrotoluene <0.01 <0.01 1,500
2,6-Dinitrotoluene <0.01 <0.01 0.349
3-Nitroaniline <0.01 <0.01 12,000
4-Bromophenylphenylether <0.01 <0.01 339
4-Chloroaniline <0.01 <0.01 12,800
4-Chlorophenylphenylether <0.01 <0.01 0.169
4-Nitroaniline <0.01 <0.01 17,600
Azobenzene <0.01 <0.01 8,520
Bis(2-chloroethoxy)methane <0.01 <0.01 0.374
Bis(2-chloroethyl)ether <0.01 <0.01 0.194
Carbazole <0.01 <0.01 0.19
Dibenzofuran <0.01 <0.01 0.568
Hexachlorobenzene <0.01 <0.01 2,000,000
Hexachlorobutadiene <0.01 <0.01 0.626
Hexachlorocyclopentadiene <0.01 <0.01 4.87
Hexachloroethane <0.01 <0.01 n/a
Isophorone <0.01 <0.01 n/a
N-nitrosodi -n-propylamine <0.01 <0.01 n/a
Nitrobenzene <0.01 <0.01 n/a
Threshold
SVOCS (mg/kg)
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 10 רשות ניקוז נחלים קישון
(S229-ו S228וט ל) PHENOLS & PHTHALATES : 5.06 טבלה
כללי מתכות -TM : 5.07 טבלה
יוצגו בדו"חות הבאים, כאשר S229 –ו S208 S226,, S228, SP227לבאצ'ים TMתוצאות עבור
.Jones UK –התוצאות ייתקבלו מ
L3סיכום
.4/10/2015 ךכללי בתארי TPHבערכי ה אחתחריג הנרשמבמהלך תקופת הדו"ח
Sample ID K3781 K3789
Lot/ Batch S228 S229
Description Cake Cake
Date 10/04/2015 15/10/2015
Phenols
2-Chlorophenol <0.01 <0.01 42,600
2-Methylphenol <0.01 <0.01 190,000
2-Nitrophenol <0.01 <0.01 11,400
2,4-Dichlorophenol <0.01 <0.01 12,800
2,4-Dimethylphenol <0.01 <0.01 85,600
2,4,5-Trichlorophenol <0.01 <0.01 428,000
2,4,6-Trichlorophenol <0.01 <0.01 4,280
4-Chloro-3-methylphenol <0.01 <0.01 428,000
4-Methylphenol <0.01 <0.01 21,200
4-Nitrophenol <0.01 <0.01 8,560
Pentachlorophenol <0.01 <0.01 429
Phenol <0.01 <0.01 470,000
Phthalates
Bis(2-ethylhexyl) phthalate 16.06 2.62 21,400
Butylbenzyl phthalate <0.01 <0.01 158,000
Di-n-butyl phthalate 0.08 <0.01 428,000
Di-n-Octyl phthalate <0.01 <0.01 180,000
Diethyl phthalate <0.01 <0.01 3,420,000
Dimethyl phthalate <0.01 <0.01 3,600,000
PHENOLS & PHTHALATES (mg/kg)
Threshold
Sample ID K3562 K3717
Lot/ Batch S190 S224
Description Cake Cake
Date 13/8/2015 20/9/2015
Aluminium 57170 47830 8,390,000
Antimony <1 <1 25
Arsenic 43 31.4 110
Beryllium 2.1 1.7 93
Cadmium 13.2 14.7 64
Chromium 138 119.6 999
Cobalt 16.5 13.9 2,550
Copper 128 120 613
Iron 47310 38950 5,960,000
Lead 36 28 160
Manganese 614 330 21,400
Nickel 56 51.7 305
Selenium 1 <1 9
Thallium <1 <1 85.2
Titanium 1400 1268 12,800,000
Vanadium 129 114 174
Zinc 443 460 3,720
Mercury CVAF <0.5 <0.5 n/a
Hexavalent
Chromium<0.3 <0.3 3,850
Threshold
TOTAL METALS (mg/kg)
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 11 רשות ניקוז נחלים קישון
6.0 L4 – לאחר ערבוב לפני ביורמידיאציהסדימנט
. SP209-ו SP225 ,SP226,SP227,SP228אספו במהלך תקופת דו"ח זה עבור באצ'יםנ L4דגימות שחמ
סימון באצ'ים: עבור באצ'ים חדשים שיפתחו לחומר שמקורו בחפירת הנחל הקידומת תמשיך להיות
S# עבור באצ'ים יעודיים לחומר שמגיע מהבריכות הישנות הקידומת תהיה ,SP# .
(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) מפורט TPH: 6.01 טבלה
(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) כללי TPH: 6.02 טבלה
* TPH Average- 1150 מעל הוא שגודלם ים'באצ עבורm3 ,1150 כל עבורm3 מורכבת דוגמא נאספת .הנתון' לבאצ הדוגמאות כל ןבי ממוצע על מבוסס הדוגמא של TPH – ה תכולת של הסופי הערך ועל
(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) pH: 6.03 טבלה
Sample IDLot/
BatchDescription
Sampled
Date>C5-C6 >C6-C8 >C8-C10
>C10-
C12
>C12-
C16
>C16-
C21
>C21-
C35
>C35-
C44Total
K3782 S226 Cake 10/06/2015 <0.1 0.2 2.6 25.4 93 75 163 31 390
K3783 S227 Cake 10/06/2015 <0.1 0.6 4.5 48 164 120 280 26 643
K3786 S228 Cake 10/11/2015 <0.1 1.6 2.9 67 183 149 507 55 966
K3787 SP225 Soil 10/12/2015 <0.1 <0.1 <0.1 <0.2 <4 <7 35 <7 35
K3788-1 SP209 Soil 13/10/2015 <0.1 <0.1 <0.1 0.9 26 86 207 30 350
K3788-2 SP209 Soil 13/10/2015 <0.1 <0.1 <0.1 <0.2 19 64 157 23 263
Aliphatics (mg/kg)
Sample IDLot/
BatchDescription
Sampled
Date>EC5-EC7 >EC7-EC8
>EC8-
EC10
>EC10-
EC12
>EC12-
EC16
>EC16-
EC21
>EC21-
EC35
>EC35-
EC44Total
K3782 S226 Cake 10/06/2015 <0.1 <0.1 0.2 <0.2 21 46 115 <7 182
K3783 S227 Cake 10/06/2015 <0.1 <0.1 0.4 <0.2 18 49 195 <7 262
K3786 S228 Cake 10/11/2015 <0.1 <0.1 0.2 <0.2 39 88 403 61 591
K3787 SP225 Soil 10/12/2015 <0.1 <0.1 <0.1 <0.2 <4 <7 36 <7 36
K3788-1 SP209 Soil 13/10/2015 <0.1 <0.1 <0.1 <0.2 <4 21 117 18 156
K3788-2 SP209 Soil 13/10/2015 <0.1 <0.1 <0.1 <0.2 <4 20 121 25 166
Aromatics mg/kg
Sample ID Lot/ Batch Description Sampled DateTotal aliphatics and
aromatics (C5-44)
Total TPH
average Threshold
K3782 S226 Cake 10/06/2015 572 - 1560
K3783 S227 Cake 10/06/2015 905 - 1560
K3786 S228 Cake 10/11/2015 1557 - 1560
K3787 SP225 Soil 10/12/2015 71 - 1560
K3788-1 SP209 Soil 13/10/2015 506 1560
K3788-2 SP209 Soil 13/10/2015 429 1560
TOTAL TPH (mg/kg)
468
K3782 K3783 K3786 K3787 K3788-1 K3788-2
S226 S227 S228 SP225 SP209 SP209
Cake Cake Cake Soil Soil Soil
10/06/2015 10/06/2015 10/11/2015 10/12/2015 13/10/2015 13/10/2015
pH 7.22 7.12 7.38 8.03 7.81 7.76 7.0 - 8.5
Threshold
Range
pH
Parameter
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 12 רשות ניקוז נחלים קישון
(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) לחות תכולת: 6.04 טבלה
(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) VOC’s: 6.05 טבלה
K3782 K3783 K3786 K3787 K3788-1 K3788-2
S226 S227 S228 SP225 SP209 SP209
Cake Cake Cake Soil Soil Soil
10/06/2015 10/06/2015 10/11/2015 10/12/2015 13/10/2015 13/10/2015
Moisture Content 41.6 50.7 49.1 16.4 14.7 14.7
Parameter
Moisture Content %
K3782 K3783 K3786 K3787 K3788-1 K3788-2
S226 S227 S228 SP225 SP209 SP209
Cake Cake Cake Soil Soil Soil
10/06/2015 10/06/2015 10/11/2015 10/12/2015 13/10/2015 13/10/2015
Dichlorodif luoromethane <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 0.672
Methy l Tertiary Buty l Ether <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 2.4
Chloromethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 1.14
Vinyl Chloride <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 0.00587
Bromomethane <0.001 <0.001 <0.001 <0.001 <0.001 <0.001 0.0897
Chloroethane <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 165
Trichlorofluoromethane <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 7.45
1,1-Dichloroethene (1,1 DCE) <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 2.71
Dichloromethane (DCM) <0.007 <0.007 <0.007 <0.007 <0.007 <0.007 0.298
trans-1-2-Dichloroethene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 4.14
1,1-Dichloroethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.0803
cis-1-2-Dichloroethene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 17,000
2,2-Dichloropropane <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 0.503
Bromochloromethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 5.16
Chloroform <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.00893
1,1,1-Trichloroethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 146
1,1-Dichloropropene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.0237
Carbon tetrachloride <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 0.011
1,2-Dichloroethane <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 0.0249
Benzene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.055
Trichloroethene (TCE) <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.0809
1,2-Dichloropropane <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 0.0466
Dibromomethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 1.28
Bromodichloromethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.0127
cis-1-3-Dichloropropene <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 2.96
Parameter Threshold
VOC (mg/kg)
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 13 רשות ניקוז נחלים קישון
(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) VOC’s: 6.05 טבלה
(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) PHENOLS & PHTHALATES: 6.06 טבלה
K3782 K3783 K3786 K3787 K3788-1 K3788-2
S226 S227 S228 SP225 SP209 SP209
Cake Cake Cake Soil Soil Soil
10/06/2015 10/06/2015 10/11/2015 10/12/2015 13/10/2015 13/10/2015
Toluene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 1,170
trans-1-3-Dichloropropene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.108
1,1,2-Trichloroethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.106
Tetrachloroethene (PCE) <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.0319
1,3-Dichloropropane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 170,000
Dibromochloromethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.0703
1,2-Dibromoethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.00387
Chlorobenzene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 26.5
1,1,1,2-Tetrachloroethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.147
Ethylbenzene 0.021 0.059 0.041 <0.003 <0.003 <0.003 0.486
p/m-Xylene 0.022 0.077 0.059 <0.006 <0.006 <0.006 43.9
o-Xylene 0.007 0.032 0.024 <0.003 <0.003 <0.003 54
Styrene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 1,140
Bromoform <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 2.57
Isopropylbenzene 0.012 0.028 0.022 <0.003 <0.003 <0.003 201
1,1,2,2-Tetrachloroethane <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 0.135
Bromobenzene <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 53.7
1,2,3-Trichloropropane <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 0.916
Propylbenzene <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 641
2-Chlorotoluene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 170,000
1,3,5-Trimethylbenzene <0.003 0.043 <0.003 <0.003 <0.003 <0.003 85,200
4-Chlorotoluene <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 170,000
tert-Butylbenzene <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 426,000
1,2,4-Trimethylbenzene 0.029 0.114 0.110 <0.006 <0.006 <0.006 5.73
sec-Butylbenzene <0.004 0.026 <0.004 <0.004 <0.004 <0.004 426,000
4-Isopropyltoluene 0.034 0.162 0.108 <0.004 <0.004 <0.004 1,060,000
1,3-Dichlorobenzene <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 2.18
1,4-Dichlorobenzene <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 0.36
n-Butylbenzene <0.004 0.148 0.116 <0.004 <0.004 <0.004 426,000
1,2-Dichlorobenzene <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 355
1,2-Dibromo-3-chloropropane <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 0.00593
Hexachlorobutadiene <0.004 <0.004 <0.004 <0.004 <0.004 <0.004 0.202
1,2,3-Trichlorobenzene <0.007 <0.007 <0.007 <0.007 <0.007 <0.007 3,420
Parameter Threshold
VOC (mg/kg)
Parameter K3782 K3783 K3786 K3787 K3788-1 K3788-2
Lot/ Batch S226 S227 S228 SP225 SP209 SP209
Description Cake Cake Cake Soil Soil Soil
Date 10/06/2015 10/06/2015 10/11/2015 10/12/2015 13/10/2015 13/10/2015
Phenols
2-Chlorophenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 42,600
2-Methylphenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 190,000
2-Nitrophenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 11,400
2,4-Dichlorophenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 12,800
2,4-Dimethylphenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 85,600
2,4,5-Trichlorophenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 428,000
2,4,6-Trichlorophenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 4,280
4-Chloro-3-methylphenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 428,000
4-Methylphenol <0.01 <0.01 0.04 <0.01 <0.01 <0.01 21,200
4-Nitrophenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 8,560
Pentachlorophenol <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 429
Phenol <0.01 0.6 <0.01 <0.01 <0.01 <0.01 470,000
Phthalates
Bis(2-ethylhexyl) phthalate 7.47 10.82 1.52 <0.01 1.11 1.34 21,400
Butylbenzyl phthalate <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 158,000
Di-n-butyl phthalate 0.03 0.03 <0.01 <0.01 <0.01 <0.01 428,000
Di-n-Octyl phthalate <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 180,000
Diethyl phthalate <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 3,420,000
Dimethyl phthalate <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 3,600,000
Threshold
PHENOLS & PHTHALATES (mg/kg)
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 14 רשות ניקוז נחלים קישון
(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) PAH’s: 6.07 טבלה
(SP209 -ו SP225, SP228, SP227,SP226 יםלוט) SVOC’s: 6.08 טבלה
Sample ID K3782 K3783 K3786 K3787 K3788-1 K3788-2
Lot/ Batch S226 S227 S228 SP225 SP209 SP209
Description Cake Cake Cake Soil Soil Soil
Date 10/06/2015 10/11/2015 10/11/2015 10/12/2015 13/10/2015 13/10/2015
2-Chloronaphthalene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 681,000
2-Methylnaphthalene 0.03 0.07 0.04 <0.01 <0.01 0.01 34,100
Naphthalene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 2.34
Acenaphthylene <0.01 <0.01 <0.01 <0.01 <0.01 0.02 235,000
Acenaphthene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 223,000
Fluorene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 149,000
Phenanthrene 0.04 0.07 0.05 <0.01 0.02 0.03 117,000
Anthracene <0.01 <0.01 <0.01 <0.01 <0.01 0.01 1,120,000
Fluoranthene <0.01 <0.01 <0.01 <0.01 0.02 0.02 149,000
Pyrene <0.01 0.03 0.02 0.02 0.04 0.05 112,000
Benzo(a)anthracene <0.01 <0.01 <0.01 0.05 0.03 0.04 350
Chrysene <0.01 <0.01 <0.01 <0.01 0.03 0.04 35,700
Benzo(bk)fluoranthene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 357
Benzo(a)pyrene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 36
Indeno(123cd)pyrene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 357
Dibenzo(ah)anthracene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 36
Benzo(ghi)perylene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 117,000
Threshold
PAH's (mg/kg)
K3782 K3783 K3786 K3787 K3788-1 K3788-2
S226 S227 S228 SP225 SP209 SP209
Cake Cake Cake Soil Soil Soil
10/06/2015 10/11/2015 10/11/2015 10/12/2015 13/10/2015 13/10/2015
1,2-Dichlorobenzene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 303
1,2,4-Trichlorobenzene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 881
1,3-Dichlorobenzene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 4,300
1,4-Dichlorobenzene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 584
2-Nitroaniline <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 5.35
2,4-Dinitrotoluene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 1,500
2,6-Dinitrotoluene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 0.349
3-Nitroaniline <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 12,000
4-Bromophenylphenylether <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 339
4-Chloroaniline <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 12,800
4-Chlorophenylphenylether <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 0.169
4-Nitroaniline <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 17,600
Azobenzene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 8,520
Bis(2-chloroethoxy)methane <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 0.374
Bis(2-chloroethyl)ether <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 0.194
Carbazole <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 0.19
Dibenzofuran <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 0.568
Hexachlorobenzene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 2,000,000
Hexachlorobutadiene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 0.626
Hexachlorocyclopentadiene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 4.87
Hexachloroethane <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 n/a
Isophorone <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 n/a
N-nitrosodi -n-propylamine <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 n/a
Nitrobenzene <0.01 <0.01 <0.01 <0.01 <0.01 <0.01 n/a
Parameter Threshold
SVOCS (mg/kg)
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 15 רשות ניקוז נחלים קישון
TM: 6.09 טבלה
יוצגו בדו"חות SP222 -ו SP213 ,SP214 ,SP215 ,SP216 ,SP217 ,SP219לבאצ' TMתוצאות עבור
.Jones UK –הבאים, כאשר התוצאות ייתקבלו מ
תשטיפים – Leachable Metals:6.10 טבלה
יוצגו SP222 -ו SP213 ,SP214 ,SP215 ,SP216 ,SP217 ,SP219לבאצ' תוצאות עבור תשטיפים
.Jones UK –בדו"חות הבאים, כאשר התוצאות ייתקבלו מ
L4סיכום
.חריגות ונרשמלא ו"חבמהלך תקופת הד
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 16 רשות ניקוז נחלים קישון
7.0 L5 – לאחר ערבוב במהלך ביורמידיאציה סדימנט
פיילוט מהוא חלק SP166 באצ'ה .SP166עבור באצ'ים L5במהלך תקופת הדו"ח נאספו שתי דוגמאות
שורות טיפול 2 –פוצל ל הבאצ'לגזם. חלופה אפשריתפטריות כאמה של קומפוסט של בדיקת הת
אחת מהשורות פוצלה באמצע, כל .טרי V3ה תוספת של קיבל מבין השתיים כאשר שורה אחת
.קיבלה תוספת גזם והמחצית השנייה תוספת קומפוסט פטריותכאשר מחצית מהשורה
. אחת טיפול שורת רק נותרה בפיילוט כן ועל אישור עברה V3 תוספת שקיבלה ההשור
(SP166 לוט) מפורט TPH: 7.01 טבלה
(SP166 לוט)כללי TPH: 7.02 טבלה
(SP166 לוט) תכולת לחות: 7.03טבלה
L5סיכום
.8/10/2015בתאריך TPHבמהלך תקופת הדו"ח נרשמה חריגה אחת בערכי
Sample IDLot/
BatchDescription
Sampled
Date>C5-C6 >C6-C8 >C8-C10
>C10-
C12
>C12-
C16
>C16-
C21
>C21-
C35 >C35-C44 Total
K3784 SP166 Soil 10/08/2015 <0.1 <0.1 <0.1 <0.2 67 275 609 108 1059
K3785 SP166 Soil 10/08/2015 <0.1 <0.1 <0.1 <0.2 68 327 636 107 1138
Aliphatics (mg/kg)
Sample IDLot/
BatchDescription
Sampled
Date
>EC5-
EC7
>EC7-
EC8
>EC8-
EC10
>EC10-
EC12
>EC12-
EC16
>EC16-
EC21
>EC21-
EC35
>EC35-
EC44Total
K3784 SP166 Soil 10/08/2015 <0.1 <0.1 <0.1 <0.2 13 103 421 56 593
K3785 SP166 Soil 10/08/2015 <0.1 <0.1 <0.1 <0.2 8 112 411 58 589
Aromatics (mg/kg)
Sample ID Lot/ Batch DescriptionSampled
Date
Total aliphatics
and aromatics
(C5-44)
Threshold
K3784 SP166 Soil 10/08/2015 1652 1560
K3785 SP166 Soil 10/08/2015 1727 1560
TOTAL TPH (mg/kg)
K3784 K3785
SP166 SP166
Soil Soil
10/08/2015 10/08/2015
Moisture
Content21.3 22.5
Parameter
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 17 רשות ניקוז נחלים קישון
0.0 L6 – נט מעורבב לאחר ביורמידיאציהסדימ
.L6במהלך תקופת הדו"ח לא נאספו דוגמאות
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 18 רשות ניקוז נחלים קישון
ולידציה סופית 0.0
, SP209 תוצאות ולידציה סופית התקבלו במהלך תקופת דו"ח זה עבור הבאצ'ים שחמ
SP225,SP226,SP227 ו- SP228.
(SP228 -ו SP209 ,SP225,SP226,SP227 )לוטים סופית ולידציה: 9.01 טבלה
Sample ID Lot/ Batch Description
Final
Validation
Location
Sampled
Date
Total aliphatics and
aromatics(C5-44)
Total TPH
average Threshold
K3782 S226 Cake L4 06/10/2015 572 - 1560
K3783 S227 Cake L4 06/10/2015 905 - 1560
K3786 S228 Cake L4 11/10/2015 1557 - 1560
K3787 SP225 Soil L4 12/10/2015 71 - 1560
K3788-1 SP209 Soil L4 13/10/2015 506 1560
K3788-2 SP209 Soil L4 13/10/2015 429 1560
TOTAL TPH mg/kg
468
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 19 רשות ניקוז נחלים קישון
10.0 V7 - ניטור איכות אויר חודשי
לאחר תוצאות יוצגו ה-Jones UK, הדוגמאות נשלחו ל, V7התבצע דיגום במהלך תקופת דו"ח זה
.Jones UK –ן מ קבלת
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 20 רשות ניקוז נחלים קישון
מאורעות ניטור חריגים 11.0
אין מאורעות חריגים לדווח.
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 21 רשות ניקוז נחלים קישון
מפרט האתר – 1נספח
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 22 רשות ניקוז נחלים קישון
: סכמת ולידציה1איור
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 23 רשות ניקוז נחלים קישון
: מפרט האתר הראשי2איור
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 24 רשות ניקוז נחלים קישון
L4 -ו L3: מיקום 3איור
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 25 רשות ניקוז נחלים קישון
(Windrows: מיקום שורות הטיפול )4איור
פרוייקט חפירה וטיפול סדימנט נחל הקישון דוח ניטור שבועי
18/10/2015 26 רשות ניקוז נחלים קישון
JONES ENVIRONMENTAL LABORATORYדו"חות ולידציה ממעבדת – 2נפסח
Unit 3 Deeside Point
Zone 3
Deeside Industrial Park
Deeside
Englobe Corp
Attention :
Date :
Your reference :
Our reference :
Location :
Date samples received :
Status :
Issue :
Dave Adams
Ha'Ashlag 27
Haifa
Israel
Registered Address : Unit 3 Deeside Point, Zone 3, Deeside Industrial Park, Deeside, CH5 2UA. UK
Jones Environmental Laboratory
CH5 2UA
Tel: +44 (0) 1244 833780
Fax: +44 (0) 1244 833781
Three samples were received for analysis on 19th August, 2015 of which one were scheduled for analysis. Please find attached our Test Report
which should be read with notes at the end of the report and should include all sections if reproduced. Interpretations and opinions are outside the
scope of any accreditation, and all results relate only to samples supplied.
All analysis is carried out on as received samples and reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected.
Simon Gomery BSc
Project Manager
4th September, 2015
Kishon
Kishon
19th August, 2015
Final report
Compiled By:
Test Report 15/11590 Batch 1 Schedule B 15/11590 Batch 1 Schedule C
1
QF-PM 3.1.1 v16Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 1 of 4
Client Name: Report : Solid
Reference:
Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub
Contact:
JE Job No.: 15/11590
J E Sample No. 3-4
Sample ID K3562
Depth
COC No / misc VS-081315-L3-1
Containers V J
Sample Date <>
Sample Type Soil
Batch Number 1
Date of Receipt 19/08/2015
Aluminium 57170AA <50 mg/kg TM30/PM15
Antimony <1 <1 mg/kg TM30/PM15
Arsenic # 43.0 <0.5 mg/kg TM30/PM15
Beryllium 2.1 <0.5 mg/kg TM30/PM15
Cadmium # 13.2 <0.1 mg/kg TM30/PM15
Chromium # 138.0 <0.5 mg/kg TM30/PM15
Cobalt # 16.5 <0.5 mg/kg TM30/PM15
Copper # 128 <1 mg/kg TM30/PM15
Iron 47310 <20 mg/kg TM30/PM15
Lead # 36 <5 mg/kg TM30/PM15
Manganese # 614 <1 mg/kg TM30/PM15
Nickel # 56.0 <0.7 mg/kg TM30/PM15
Selenium # 1 <1 mg/kg TM30/PM15
Thallium <1 <1 mg/kg TM30/PM15
Titanium 1400 <5 mg/kg TM30/PM15
Vanadium 129 <1 mg/kg TM30/PM15
Water Soluble Boron # 27.3 <0.1 mg/kg TM74/PM32
Zinc # 443 <5 mg/kg TM30/PM15
Mercury CVAF <0.5 <0.5 mg/kg TM61/PM62
Hexavalent Chromium # <0.3 <0.3 mg/kg TM38/PM20
Jones Environmental Laboratory
Englobe Corp
Kishon
Kishon
Dave Adams
Please see attached notes for all
abbreviations and acronyms
LOD/LOR UnitsMethod
No.
QF-PM 3.1.2 v11Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 2 of 4
JE Job No.:
SOILS
DEVIATING SAMPLES
SURROGATES
DILUTIONS
NOTE
JE Job No.:
#
B
DR
M
NA
NAD
ND
NDP
SS
SV
W
+
++
*
AD
CO
LOD/LOR
ME
NFD
BS
LB
N
TB
OC
AA
Trip Blank Sample
AQC Sample
Samples must be received in a condition appropriate to the requested analyses. All samples should be submitted to the laboratory in suitable
containers with sufficient ice packs to sustain an appropriate temperature for the requested analysis. If this is not the case you will be informed and
any test results that may be compromised highlighted on your deviating samples report.
MCERTS accredited.
ISO17025 (UKAS) accredited - UK.
15/11590
AQC failure, accreditation has been removed from this result, if appropriate, see 'Note' on previous page.
Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.
Please note we are not a UK Drinking Water Inspectorate (DWI) Approved Laboratory .
ISO17025 (UKAS) accreditation applies to surface water and groundwater and one other matrix which is analysis specific, any other liquids are
outside our scope of accreditation.
Blank Sample
Client Sample
Analysis subcontracted to a Jones Environmental approved laboratory.
Calibrated against a single substance
Not applicable
Suspected carry over
ABBREVIATIONS and ACRONYMS USED
Samples are dried at 35°C ±5°C
Indicates analyte found in associated method blank.
No Asbestos Detected.
No Determination Possible
NOTES TO ACCOMPANY ALL SCHEDULES AND REPORTS
Please note we are only MCERTS accredited (UK soils only) for sand, loam and clay and any other matrix is outside our scope of accreditation.
Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.
15/11590
WATERS
Where an MCERTS report has been requested, you will be notified within 48 hours of any samples that have been identified as being outside our
MCERTS scope. As validation has been performed on clay, sand and loam, only samples that are predominantly these matrices, or combinations
of them will be within our MCERTS scope. If samples are not one of a combination of the above matrices they will not be marked as MCERTS
accredited.
Where appropriate please make sure that our detection limits are suitable for your needs, if they are not, please notify us immediately.
It is assumed that you have taken representative samples on site and require analysis on a representative subsample. Stones will generally be
included unless we are requested to remove them.
If you have not already done so, please send us a purchase order if this is required by your company.
% Asbestos in Asbestos Containing Materials (ACMs) is determined by reference to HSG 264 The Survey Guide - Appendix 2 : ACMs in buildings
listed in order of ease of fibre release.
All analysis is reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected. Samples are dried at 35°C ±5°C unless
otherwise stated. Moisture content for CEN Leachate tests are dried at 105°C ±5°C.
x5 Dilution
Where a CEN 10:1 ZERO Headspace VOC test has been carried out, a 10:1 ratio of water to wet (as received) soil has been used.
All samples will be discarded one month after the date of reporting, unless we are instructed to the contrary.
Surrogate compounds are added during the preparation process to monitor recovery of analytes. However low recovery in soils is often due to
peat, clay or other organic rich matrices. For waters this can be due to oxidants, surfactants, organic rich sediments or remediation fluids.
Acceptable limits for most organic methods are 70 - 130% and for VOCs are 50 - 150%. When surrogate recoveries are outside the performance
criteria but the associated AQC passes this is assumed to be due to matrix effect. Results are not surrogate corrected.
A dilution suffix indicates a dilution has been performed and the reported result takes this into account. No further calculation is required.
Outside Calibration Range
No Fibres Detected
Result outside calibration range, results should be considered as indicative only and are not accredited.
Results expressed on as received basis.
Surrogate recovery outside performance criteria. This may be due to a matrix effect.
Data is only reported if the laboratory is confident that the data is a true reflection of the samples analysed. Data is only reported as accredited
when all the requirements of our Quality System have been met. In certain circumstances where all the requirements of the Quality System have
not been met, for instance if the associated AQC has failed, the reason is fully investigated and documented. The sample data is then evaluated
alongside the other quality control checks performed during analysis to determine its suitability. Following this evaluation, provided the sample
results have not been effected, the data is reported but accreditation is removed. It is a UKAS requirement for data not reported as accredited to
be considered indicative only, but this does not mean the data is not valid.
Where possible, and if requested, samples will be re-extracted and a revised report issued with accredited results. Please do not hesitate to
contact the laboratory if further details are required of the circumstances which have led to the removal of accreditation.
Matrix Effect
As surface waters require different sample preparation to groundwaters the laboratory must be informed of the water type when submitting
samples.
None Detected (usually refers to VOC and/SVOC TICs).
Limit of Detection (Limit of Reporting) in line with ISO 17025 and MCERTS
Dilution required.
QF-PM 3.1.9 v31Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 3 of 4
JE Job No: 15/11590
Test Method No. Description
Prep Method
No. (if
appropriate)
Description
ISO
17025
(UKAS)
MCERTS
(UK soils
only)
Analysis done
on As Received
(AR) or Dried
(AD)
Reported on
dry weight
basis
TM30Determination of Trace Metal elements by ICP-OES (Inductively Coupled Plasma -
Optical Emission Spectrometry). Modified US EPA Method 200.7PM15
Acid digestion of dried and ground solid samples using Aqua Regia refluxed at 112.5
°C. Samples containing asbestos are not dried and ground.AD Yes
TM30Determination of Trace Metal elements by ICP-OES (Inductively Coupled Plasma -
Optical Emission Spectrometry). Modified US EPA Method 200.7PM15
Acid digestion of dried and ground solid samples using Aqua Regia refluxed at 112.5
°C. Samples containing asbestos are not dried and ground.Yes AD Yes
TM38Soluble Ion analysis using the Thermo Aquakem Photometric Automatic Analyser.
Modified US EPA methods 325.2, 375.4, 365.2, 353.1, 354.1PM20
Extraction of dried and ground samples with deionised water in a 2:1 water to solid
ratio for anions. Extraction of as received samples with deionised water in a 2:1 water
to solid ratio for ammoniacal nitrogen. Samples are extracted using an orbital shaker.
Yes AR Yes
TM61Modified US EPA methods 245.7 and 200.7. Determination of Mercury by Cold Vapour
Atomic Fluorescence. PM62 Acid digestion of as received solid samples using Aqua Regia refluxed at 112.5 °C. AR Yes
TM74 Analysis of water soluble boron (20:1 extract) by ICP-OES. PM32 Hot water soluble boron is extracted from dried and ground samples using a 20:1 ratio. Yes AD Yes
Jones Environmental Laboratory Method Code Appendix
QF-PM 3.1.10 v14 Please include all sections of this report if it is reproduced 4 of 4
Unit 3 Deeside Point
Zone 3
Deeside Industrial Park
Deeside
A.D. Edan Hadash
Attention :
Date :
Your reference :
Our reference :
Location :
Date samples received :
Status :
Issue :
Dave Adams
Kishon Project
Ha'Ashlag 30
Haifa
3295163
Israel
Registered Address : Unit 3 Deeside Point, Zone 3, Deeside Industrial Park, Deeside, CH5 2UA. UK
Jones Environmental Laboratory
CH5 2UA
Tel: +44 (0) 1244 833780
Fax: +44 (0) 1244 833781
Eighteen samples were received for analysis on 9th October, 2015 of which eighteen were scheduled for analysis. Please find attached our Test
Report which should be read with notes at the end of the report and should include all sections if reproduced. Interpretations and opinions are
outside the scope of any accreditation, and all results relate only to samples supplied.
All analysis is carried out on as received samples and reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected.
Simon Gomery BSc
Project Manager
14th October, 2015
Kishon
9th October, 2015
Final report
Compiled By:
Test Report 15/14490 Batch 1
1
QF-PM 3.1.1 v16Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 1 of 10
Client Name: Report : Solid
Reference:
Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub
Contact:
JE Job No.: 15/14490
J E Sample No. 1 2 3 4 5 6 7 8 9 10
Sample ID K3717 K3718 K3729-1 K3729-2 K3730-1 K3730-2 K3731-1 K3731-2 K3732-1 K3732-2
Depth
COC No / misc VS-092015-L3-1 VS-092015-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092415-L4-1 VS-092415-L4-1
Containers B B B B B B B B B B
Sample Date 20/09/2015 20/09/2015 21/09/2015 21/09/2015 21/09/2015 21/09/2015 21/09/2015 21/09/2015 24/09/2015 24/09/2015
Sample Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil
Batch Number 1 1 1 1 1 1 1 1 1 1
Date of Receipt 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015
Aluminium 47830 37280 35510 37090 42760 41960 46380 44240 47790 42810 <50 mg/kg TM30/PM15
Antimony <1 <1 <1 1 1 1 1 2 1 <1 <1 mg/kg TM30/PM15
Arsenic # 31.4 26.4 6.2 5.3 7.1 6.0 13.6 10.6 14.9 8.6 <0.5 mg/kg TM30/PM15
Beryllium 1.7 1.4 1.3 1.4 1.7 1.6 1.7 1.8 1.9 1.6 <0.5 mg/kg TM30/PM15
Cadmium # 14.7 8.1 2.6 2.4 3.8 1.7 15.6 14.8 11.9 6.8 <0.1 mg/kg TM30/PM15
Chromium # 119.6 100.9 67.2 72.7 84.0 75.5 120.9 122.2 117.7 92.6 <0.5 mg/kg TM30/PM15
Cobalt # 13.9 11.3 16.1 16.4 18.5 19.6 16.4 17.2 17.9 16.6 <0.5 mg/kg TM30/PM15
Copper # 120 80 41 39 44 34 127 119 102 63 <1 mg/kg TM30/PM15
Iron 38950 30740 33080 34570 40520 40100 37960 38610 42760 37990 <20 mg/kg TM30/PM15
Lead # 28 24 8 7 9 7 21 29 20 13 <5 mg/kg TM30/PM15
Manganese # 330 301 650 594 722 696 528 592 595 623 <1 mg/kg TM30/PM15
Nickel # 51.7 40.7 42.9 45.0 51.6 51.9 54.7 53.8 56.0 48.6 <0.7 mg/kg TM30/PM15
Selenium # <1 <1 <1 <1 <1 <1 <1 1 <1 <1 <1 mg/kg TM30/PM15
Thallium <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 <1 mg/kg TM30/PM15
Titanium 1268 988 1077 1194 1128 1333 1329 1121 1202 1231 <5 mg/kg TM30/PM15
Vanadium 114 85 74 77 91 87 126 124 122 94 <1 mg/kg TM30/PM15
Water Soluble Boron # 21.6 16.4 6.3 4.9 6.1 6.8 8.7 4.4 5.1 10.2 <0.1 mg/kg TM74/PM32
Zinc # 460 294 122 123 153 116 463 420 349 224 <5 mg/kg TM30/PM15
Mercury CVAF <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 <0.5 mg/kg TM61/PM62
Natural Moisture Content 210.1 75.2 20.7 17.6 21.8 23.6 33.3 33.5 28.6 20.9 <0.1 % PM4/PM0
Hexavalent Chromium # <0.3 0.7 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 mg/kg TM38/PM20
Please see attached notes for all
abbreviations and acronyms
LOD/LOR UnitsMethod
No.
Jones Environmental Laboratory
A.D. Edan Hadash
Kishon
Dave Adams
QF-PM 3.1.2 v11Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 2 of 10
Client Name: Report : Solid
Reference:
Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub
Contact:
JE Job No.: 15/14490
J E Sample No. 11 12 13 14 15 16 17 18
Sample ID K3733 K3734-1 K3734-2 K3735-1 K3735-2 K3736-1 K3736-2 K3752
Depth
COC No / misc VS-092415-L4-1 VS-092415-L4-1 VS-092415-L4-1 VS-092915-L4-1 VS-092915-L4-1 VS-092915-L4-1 VS-092915-L4-1 VS-093015-L3-1
Containers B B B B B B B B
Sample Date 24/09/2015 24/09/2015 24/09/2015 29/09/2015 29/09/2015 29/09/2015 29/09/2015 30/09/2015
Sample Type Soil Soil Soil Soil Soil Soil Soil Soil
Batch Number 1 1 1 1 1 1 1 1
Date of Receipt 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015
Aluminium 32700 43960 47110 36640 34670 40210 38030 40850 <50 mg/kg TM30/PM15
Antimony 1 <1 <1 <1 <1 <1 <1 <1 <1 mg/kg TM30/PM15
Arsenic # 10.6 19.0 11.7 12.3 12.6 18.9 21.0 26.4 <0.5 mg/kg TM30/PM15
Beryllium 1.2 1.6 1.7 1.4 1.4 1.5 1.5 1.4 <0.5 mg/kg TM30/PM15
Cadmium # 5.7 7.0 5.9 7.3 7.9 8.1 8.2 9.1 <0.1 mg/kg TM30/PM15
Chromium # 73.3 93.2 91.1 86.9 94.4 96.6 99.9 95.2 <0.5 mg/kg TM30/PM15
Cobalt # 12.9 15.4 18.0 14.2 12.9 13.5 13.2 12.4 <0.5 mg/kg TM30/PM15
Copper # 55 76 60 71 77 79 84 89 <1 mg/kg TM30/PM15
Iron 28960 36510 40380 31910 29870 33470 33320 33250 <20 mg/kg TM30/PM15
Lead # 12 17 11 16 19 19 22 23 <5 mg/kg TM30/PM15
Manganese # 430 484 604 451 423 401 429 319 <1 mg/kg TM30/PM15
Nickel # 37.7 47.8 52.9 42.5 41.0 44.1 42.1 43.6 <0.7 mg/kg TM30/PM15
Selenium # <1 <1 <1 <1 <1 <1 <1 <1 <1 mg/kg TM30/PM15
Thallium <1 <1 <1 <1 <1 <1 <1 <1 <1 mg/kg TM30/PM15
Titanium 953 1277 1347 1111 915 1182 1008 1110 <5 mg/kg TM30/PM15
Vanadium 75 95 99 87 88 92 92 93 <1 mg/kg TM30/PM15
Water Soluble Boron # 8.8 14.1 12.0 9.6 10.5 11.6 15.4 19.9 <0.1 mg/kg TM74/PM32
Zinc # 197 269 214 250 276 280 294 323 <5 mg/kg TM30/PM15
Mercury CVAF <0.5 <0.5 <0.5 0.7 <0.5 <0.5 <0.5 <0.5 <0.5 mg/kg TM61/PM62
Natural Moisture Content 25.9 38.2 32.7 35.0 34.7 49.0 46.5 151.6 <0.1 % PM4/PM0
Hexavalent Chromium # <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 <0.3 mg/kg TM38/PM20
LOD/LOR UnitsMethod
No.
Jones Environmental Laboratory
A.D. Edan Hadash
Kishon
Dave Adams
Please see attached notes for all
abbreviations and acronyms
QF-PM 3.1.2 v11Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 3 of 10
Client Name: Report : CEN 10:1 1 Batch
Reference:
Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub
Contact:
JE Job No.: 15/14490
J E Sample No. 2 3 4 5 6 7 8 9 10 11
Sample ID K3718 K3729-1 K3729-2 K3730-1 K3730-2 K3731-1 K3731-2 K3732-1 K3732-2 K3733
Depth
COC No / misc VS-092015-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092115-L4-1 VS-092415-L4-1 VS-092415-L4-1 VS-092415-L4-1
Containers B B B B B B B B B B
Sample Date 20/09/2015 21/09/2015 21/09/2015 21/09/2015 21/09/2015 21/09/2015 21/09/2015 24/09/2015 24/09/2015 24/09/2015
Sample Type Soil Soil Soil Soil Soil Soil Soil Soil Soil Soil
Batch Number 1 1 1 1 1 1 1 1 1 1
Date of Receipt 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015
Dissolved Antimony # <0.002 0.002 <0.002 0.003 0.002 0.003 0.004 0.003 0.003 <0.002 <0.002 mg/l TM30/PM17
Dissolved Arsenic # 0.0159 0.0029 <0.0025 <0.0025 <0.0025 <0.0025 <0.0025 0.0031 <0.0025 <0.0025 <0.0025 mg/l TM30/PM17
Dissolved Beryllium # <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 mg/l TM30/PM17
Dissolved Cadmium # <0.0005 <0.0005 0.0007 <0.0005 0.0009 0.0034 0.0045 0.0012 0.0025 0.0010 <0.0005 mg/l TM30/PM17
Dissolved Chromium # <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 mg/l TM30/PM17
Dissolved Cobalt # <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 <0.002 mg/l TM30/PM17
Dissolved Copper # <0.007 0.013 0.018 0.012 0.012 0.024 0.031 0.011 0.019 0.013 <0.007 mg/l TM30/PM17
Dissolved Lead # <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 mg/l TM30/PM17
Dissolved Manganese # 0.163 0.007 0.008 0.099 0.045 0.091 0.086 0.148 0.042 0.075 <0.002 mg/l TM30/PM17
Dissolved Nickel # 0.015 0.004 0.005 0.006 0.005 0.009 0.012 0.007 0.007 0.006 <0.002 mg/l TM30/PM17
Dissolved Selenium # <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 mg/l TM30/PM17
Dissolved Thallium # <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 mg/l TM30/PM17
Dissolved Vanadium # 0.0094 0.0160 0.0182 0.0165 0.0129 0.0312 0.0352 0.0244 0.0244 0.0153 <0.0015 mg/l TM30/PM17
Dissolved Zinc # 0.004 0.007 0.009 0.008 0.007 0.022 0.028 0.019 0.015 0.010 <0.003 mg/l TM30/PM17
Mercury Dissolved by CVAF # 0.00007 0.00004 0.00008 0.00002 0.00003 0.00008 0.00011 0.00008 0.00006 0.00004 <0.00001 mg/l TM61/PM38
Mass of raw test portion 0.167 0.1091 0.1112 0.1168 0.1177 0.1249 0.1273 0.1173 0.1144 0.119 kg NONE/PM17
Leachant Volume 0.823 0.881 0.879 0.873 0.872 0.866 0.862 0.872 0.875 0.871 l NONE/PM17
Hexavalent Chromium <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 mg/l TM38/PM0
Please see attached notes for all
abbreviations and acronyms
LOD/LOR UnitsMethod
No.
Jones Environmental Laboratory
A.D. Edan Hadash
Kishon
Dave Adams
QF-PM 3.1.2 v11Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 4 of 10
Client Name: Report : CEN 10:1 1 Batch
Reference:
Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub
Contact:
JE Job No.: 15/14490
J E Sample No. 12 13 14 15 16 17
Sample ID K3734-1 K3734-2 K3735-1 K3735-2 K3736-1 K3736-2
Depth
COC No / misc VS-092415-L4-1 VS-092415-L4-1 VS-092915-L4-1 VS-092915-L4-1 VS-092915-L4-1 VS-092915-L4-1
Containers B B B B B B
Sample Date 24/09/2015 24/09/2015 29/09/2015 29/09/2015 29/09/2015 29/09/2015
Sample Type Soil Soil Soil Soil Soil Soil
Batch Number 1 1 1 1 1 1
Date of Receipt 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015 09/10/2015
Dissolved Antimony # <0.002 <0.002 0.003 <0.002 <0.002 0.002 <0.002 mg/l TM30/PM17
Dissolved Arsenic # <0.0025 <0.0025 0.0028 0.0033 0.0052 <0.0025 <0.0025 mg/l TM30/PM17
Dissolved Beryllium # <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 <0.0005 mg/l TM30/PM17
Dissolved Cadmium # 0.0006 0.0007 <0.0005 0.0009 0.0005 <0.0005 <0.0005 mg/l TM30/PM17
Dissolved Chromium # <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 <0.0015 mg/l TM30/PM17
Dissolved Cobalt # <0.002 <0.002 <0.002 <0.002 0.003 0.002 <0.002 mg/l TM30/PM17
Dissolved Copper # 0.009 0.008 <0.007 0.008 <0.007 <0.007 <0.007 mg/l TM30/PM17
Dissolved Lead # <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 <0.005 mg/l TM30/PM17
Dissolved Manganese # 0.032 0.074 0.436 0.231 0.914 0.587 <0.002 mg/l TM30/PM17
Dissolved Nickel # 0.005 0.004 0.009 0.008 0.009 0.008 <0.002 mg/l TM30/PM17
Dissolved Selenium # <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 mg/l TM30/PM17
Dissolved Thallium # <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 <0.003 mg/l TM30/PM17
Dissolved Vanadium # 0.0147 0.0128 0.0188 0.0195 0.0105 0.0128 <0.0015 mg/l TM30/PM17
Dissolved Zinc # 0.009 0.007 0.010 0.014 <0.003 0.006 <0.003 mg/l TM30/PM17
Mercury Dissolved by CVAF # 0.00003 0.00001 0.00007 0.00008 0.00005 0.00009 <0.00001 mg/l TM61/PM38
Mass of raw test portion 0.1241 0.1188 0.1271 0.1221 0.145 0.1338 kg NONE/PM17
Leachant Volume 0.866 0.871 0.863 0.868 0.845 0.857 l NONE/PM17
Hexavalent Chromium <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 <0.006 mg/l TM38/PM0
LOD/LOR UnitsMethod
No.
Jones Environmental Laboratory
A.D. Edan Hadash
Kishon
Dave Adams
Please see attached notes for all
abbreviations and acronyms
QF-PM 3.1.2 v11Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 5 of 10
Notification of Deviating Samples
J E
Job
No.
Batch Depth J E Sample
No.Analysis Reason
Please note that only samples that are deviating are mentioned in this report. If no samples are listed it is because none were deviating.
Only analyses which are accredited are recorded as deviating if set criteria are not met.
Jones Environmental Laboratory
Kishon
Dave AdamsContact:
Sample ID
Client Name: A.D. Edan Hadash
Reference:
Location:
No deviating sample report results for job 15/14490
QF-PM 3.1.11 v3 Please include all sections of this report if it is reproduced 6 of 10
JE Job No.:
SOILS
DEVIATING SAMPLES
SURROGATES
DILUTIONS
NOTE
Surrogate compounds are added during the preparation process to monitor recovery of analytes. However low recovery in soils is often due to
peat, clay or other organic rich matrices. For waters this can be due to oxidants, surfactants, organic rich sediments or remediation fluids.
Acceptable limits for most organic methods are 70 - 130% and for VOCs are 50 - 150%. When surrogate recoveries are outside the performance
criteria but the associated AQC passes this is assumed to be due to matrix effect. Results are not surrogate corrected.
A dilution suffix indicates a dilution has been performed and the reported result takes this into account. No further calculation is required.
Where appropriate please make sure that our detection limits are suitable for your needs, if they are not, please notify us immediately.
ISO17025 (UKAS) accreditation applies to surface water and groundwater and one other matrix which is analysis specific, any other liquids are
outside our scope of accreditation.
As surface waters require different sample preparation to groundwaters the laboratory must be informed of the water type when submitting
samples.
% Asbestos in Asbestos Containing Materials (ACMs) is determined by reference to HSG 264 The Survey Guide - Appendix 2 : ACMs in buildings
listed in order of ease of fibre release.
All analysis is reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected. Samples are dried at 35°C ±5°C
unless otherwise stated. Moisture content for CEN Leachate tests are dried at 105°C ±5°C.
Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.
Please note we are not a UK Drinking Water Inspectorate (DWI) Approved Laboratory .
Negative Neutralization Potential (NP) values are obtained when the volume of NaOH (0.1N) titrated (pH 8.3) is greater than the volume of HCl
(1N) to reduce the pH of the sample to 2.0 - 2.5. Any negative NP values are corrected to 0.
Where a CEN 10:1 ZERO Headspace VOC test has been carried out, a 10:1 ratio of water to wet (as received) soil has been used.
Samples must be received in a condition appropriate to the requested analyses. All samples should be submitted to the laboratory in suitable
containers with sufficient ice packs to sustain an appropriate temperature for the requested analysis. If this is not the case you will be informed
and any test results that may be compromised highlighted on your deviating samples report.
NOTES TO ACCOMPANY ALL SCHEDULES AND REPORTS
Please note we are only MCERTS accredited (UK soils only) for sand, loam and clay and any other matrix is outside our scope of accreditation.
Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.
15/14490
WATERS
Where an MCERTS report has been requested, you will be notified within 48 hours of any samples that have been identified as being outside our
MCERTS scope. As validation has been performed on clay, sand and loam, only samples that are predominantly these matrices, or combinations
of them will be within our MCERTS scope. If samples are not one of a combination of the above matrices they will not be marked as MCERTS
accredited.
It is assumed that you have taken representative samples on site and require analysis on a representative subsample. Stones will generally be
included unless we are requested to remove them.
All samples will be discarded one month after the date of reporting, unless we are instructed to the contrary.
If you have not already done so, please send us a purchase order if this is required by your company.
QF-PM 3.1.9 v32Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 7 of 11
Data is only reported if the laboratory is confident that the data is a true reflection of the samples analysed. Data is only reported as accredited
when all the requirements of our Quality System have been met. In certain circumstances where all the requirements of the Quality System have
not been met, for instance if the associated AQC has failed, the reason is fully investigated and documented. The sample data is then evaluated
alongside the other quality control checks performed during analysis to determine its suitability. Following this evaluation, provided the sample
results have not been effected, the data is reported but accreditation is removed. It is a UKAS requirement for data not reported as accredited to
be considered indicative only, but this does not mean the data is not valid.
Where possible, and if requested, samples will be re-extracted and a revised report issued with accredited results. Please do not hesitate to
contact the laboratory if further details are required of the circumstances which have led to the removal of accreditation.
QF-PM 3.1.9 v32Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 8 of 11
JE Job No.:
#
B
DR
M
NA
NAD
ND
NDP
SS
SV
W
+
++
*
AD
CO
LOD/LOR
ME
NFD
BS
LB
N
TB
OC
MCERTS accredited.
ISO17025 (UKAS) accredited - UK.
15/14490
AQC failure, accreditation has been removed from this result, if appropriate, see 'Note' on previous page.
Calibrated against a single substance
Not applicable
No Asbestos Detected.
No Determination Possible
Indicates analyte found in associated method blank.
None Detected (usually refers to VOC and/SVOC TICs).
Outside Calibration Range
No Fibres Detected
Result outside calibration range, results should be considered as indicative only and are not accredited.
Results expressed on as received basis.
Surrogate recovery outside performance criteria. This may be due to a matrix effect.
Limit of Detection (Limit of Reporting) in line with ISO 17025 and MCERTS
Analysis subcontracted to a Jones Environmental approved laboratory.
Matrix Effect
Blank Sample
Client Sample
Trip Blank Sample
AQC Sample
Suspected carry over
ABBREVIATIONS and ACRONYMS USED
Samples are dried at 35°C ±5°C
Dilution required.
QF-PM 3.1.9 v32Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 9 of 11
JE Job No: 15/14490
Test Method No. Description
Prep Method
No. (if
appropriate)
Description
ISO
17025
(UKAS)
MCERTS
(UK soils
only)
Analysis done
on As Received
(AR) or Dried
(AD)
Reported on
dry weight
basis
PM4Gravimetric measurement of Natural Moisture Content and % Moisture Content at
either 35°C or 105°C. Calculation based on ISO 11465 and BS1377.PM0 No preparation is required.
TM30Determination of Trace Metal elements by ICP-OES (Inductively Coupled Plasma -
Optical Emission Spectrometry). Modified US EPA Method 200.7PM15
Acid digestion of dried and ground solid samples using Aqua Regia refluxed at 112.5
°C. Samples containing asbestos are not dried and ground.AD Yes
TM30Determination of Trace Metal elements by ICP-OES (Inductively Coupled Plasma -
Optical Emission Spectrometry). Modified US EPA Method 200.7PM15
Acid digestion of dried and ground solid samples using Aqua Regia refluxed at 112.5
°C. Samples containing asbestos are not dried and ground.Yes AD Yes
TM30Determination of Trace Metal elements by ICP-OES (Inductively Coupled Plasma -
Optical Emission Spectrometry). Modified US EPA Method 200.7PM17
Modified method EN12457-2 As received solid samples are leached with water in a
10:1 water to soil ratio for 24 hours, the moisture content of the sample is included in
the ratio.
Yes AR Yes
TM38Soluble Ion analysis using the Thermo Aquakem Photometric Automatic Analyser.
Modified US EPA methods 325.2, 375.4, 365.2, 353.1, 354.1PM0 No preparation is required. AR Yes
TM38Soluble Ion analysis using the Thermo Aquakem Photometric Automatic Analyser.
Modified US EPA methods 325.2, 375.4, 365.2, 353.1, 354.1PM20
Extraction of dried and ground samples with deionised water in a 2:1 water to solid
ratio for anions. Extraction of as received samples with deionised water in a 2:1 water
to solid ratio for ammoniacal nitrogen. Samples are extracted using an orbital shaker.
Yes AR Yes
TM61Modified US EPA methods 245.7 and 200.7. Determination of Mercury by Cold Vapour
Atomic Fluorescence. PM38
Samples are brominated to reduce all mercury compounds to Mercury (II) which is
analysed using method TM061.Yes AR Yes
TM61Modified US EPA methods 245.7 and 200.7. Determination of Mercury by Cold Vapour
Atomic Fluorescence. PM62 Acid digestion of as received solid samples using Aqua Regia refluxed at 112.5 °C. AR Yes
TM74 Analysis of water soluble boron (20:1 extract) by ICP-OES. PM32 Hot water soluble boron is extracted from dried and ground samples using a 20:1 ratio. Yes AD Yes
NONE No Method Code PM17
Modified method EN12457-2 As received solid samples are leached with water in a
10:1 water to soil ratio for 24 hours, the moisture content of the sample is included in
the ratio.
Jones Environmental Laboratory Method Code Appendix
QF-PM 3.1.10 v14 Please include all sections of this report if it is reproduced 10 of 10
Client Name: Report : Solid
Reference:
Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub
Contact:
JE Job No.: 15/688
J E Sample No. 1 4 5 6 7 10 13
Sample ID K3753 K3754 K3755 K3780 K3782 K3783 K3781
Depth
COC No / misc VS-093015-L4-1 VS-093015-L5-PT1-2 VS-093015-L5-PT2-2 VS-100115-L3-1 VS-100615-L4-1 VS-100615-L4-1 VS-100415-L3-1
Containers T T T T T T T
Sample Date 30/09/2015 30/09/2015 30/09/2015 01/10/2015 06/10/2015 06/10/2015 06/10/2015
Sample Type Solid Solid Solid Solid Solid Solid Solid
Batch Number 1 1 1 1 1 1 1
Date of Receipt 06/10/2015 06/10/2015 06/10/2015 06/10/2015 06/10/2015 06/10/2015 06/10/2015
TPH CWG
Aliphatics
>C5-C6 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12
>C6-C8 0.2 <0.1 <0.1 1.2 0.2 0.6 0.6 <0.1 mg/kg TM36/PM12
>C8-C10 2.2 <0.1 <0.1 5.7 2.6 4.5 5.6 <0.1 mg/kg TM36/PM12
>C10-C12 31.3 <0.2 <0.2 232.8 25.4 48.0 197.9 <0.2 mg/kg TM5/PM16
>C12-C16 102 76 72 756 93 164 570 <4 mg/kg TM5/PM16
>C16-C21 77 258 361 567 75 120 446 <7 mg/kg TM5/PM16
>C21-C35 160 576 756 1401 163 280 1087 <7 mg/kg TM5/PM16
>C35-C44 13 82 103 165 31 26 178 <7 mg/kg TM5/PM16
Total aliphatics C5-44 386 992 1292 3129 390 643 2485 <26 mg/kg TM5/TM36/PM16
Aromatics
>C5-EC7 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12
>EC7-EC8 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12
>EC8-EC10 0.2 <0.1 <0.1 0.9 0.2 0.4 0.6 <0.1 mg/kg TM36/PM12
>EC10-EC12 <0.2 <0.2 <0.2 <0.2 <0.2 48.0 <0.2 <0.2 mg/kg TM5/PM16
>EC12-EC16 42 12 <4 141 21 164 33 <4 mg/kg TM5/PM16
>EC16-EC21 55 109 121 267 46 120 137 <7 mg/kg TM5/PM16
>EC21-EC35 179 430 497 1095 115 280 564 <7 mg/kg TM5/PM16
>EC35-EC44 20 86 95 162 <7 26 77 <7 mg/kg TM5/PM16
Total aromatics C5-44 296 637 713 1666 182 638 812 <26 mg/kg TM5/TM36/PM16
Total aliphatics and aromatics(C5-44) 682 1629 2005 4795 572 1281 3297 <52 mg/kg TM5/TM36/PM16
Natural Moisture Content 82.2 22.8 20.6 200.0 71.3 102.7 197.1 <0.1 % PM4/PM0
Moisture Content 45.1 18.6 17.1 66.7 41.6 50.7 66.3 <0.1 % PM4/PM0
pH 7.14 - - - 7.22 7.12 - <0.01 pH units TM19/PM11
Please see attached notes for all
abbreviations and acronyms
LOD UnitsMethod
No.
Jones Environmental Laboratory
Kishon Project
David Adams
QF-PM 3.1.2 v10Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 1 of 1
Ha’Ashlag 27
Haifa
Israel
3295163
Kishon Project
Attention :
Date :
Your reference :
Our reference :
Location :
Date samples received :
Status :
Issue :
David Adams
Haifa
Israel
Registered Address : Unit 3 Deeside Point, Zone 3, Deeside Industrial Park, Deeside, CH5 2UA. UK
Jones Environmental Laboratory
Tel: +972 58 401 0455
Two samples were received for analysis on 8th October, 2015. Please find attached our Test Report which should be read with notes at the end of
the report and should include all sections if reproduced. Interpretations and opinions are outside the scope of any accreditation, and all results relate
only to samples supplied.
All analysis is carried out on as received samples and reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected.
Dave Adams
Site Scientist
12th October, 2015
8th October, 2015
Final report
Compiled By:
Test Report 15/689 Batch 1
1
QF-PM 3.1.1 v15Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 1 of 4
Client Name: Report : Solid
Reference:
Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub
Contact:
JE Job No.: 15/689
J E Sample No. 1 2
Sample ID K3784 K3785
Depth
COC No / misc VS-100815-L5-PT1-3 VS-100815-L5-PT2-3
Containers T T
Sample Date 08/10/2015 08/10/2015
Sample Type Solid Solid
Batch Number 1 1
Date of Receipt 08/10/2015 08/10/2015
TPH CWG
Aliphatics
>C5-C6 <0.1 <0.1 <0.1 mg/kg TM36/PM12
>C6-C8 <0.1 <0.1 <0.1 mg/kg TM36/PM12
>C8-C10 <0.1 <0.1 <0.1 mg/kg TM36/PM12
>C10-C12 <0.2 <0.2 <0.2 mg/kg TM5/PM16
>C12-C16 67 68 <4 mg/kg TM5/PM16
>C16-C21 275 327 <7 mg/kg TM5/PM16
>C21-C35 609 636 <7 mg/kg TM5/PM16
>C35-C44 108 107 <7 mg/kg TM5/PM16
Total aliphatics C5-44 1059 1138 <26 mg/kg TM5/TM36/PM16
Aromatics
>C5-EC7 <0.1 <0.1 <0.1 mg/kg TM36/PM12
>EC7-EC8 <0.1 <0.1 <0.1 mg/kg TM36/PM12
>EC8-EC10 <0.1 <0.1 <0.1 mg/kg TM36/PM12
>EC10-EC12 <0.2 <0.2 <0.2 mg/kg TM5/PM16
>EC12-EC16 13 8 <4 mg/kg TM5/PM16
>EC16-EC21 103 112 <7 mg/kg TM5/PM16
>EC21-EC35 421 411 <7 mg/kg TM5/PM16
>EC35-EC44 56 58 <7 mg/kg TM5/PM16
Total aromatics C5-44 593 589 <26 mg/kg TM5/TM36/PM16
Total aliphatics and aromatics(C5-44) 1652 1727 <52 mg/kg TM5/TM36/PM16
Natural Moisture Content 27.1 29.1 <0.1 % PM4/PM0
Moisture Content 21.3 22.5 <0.1 % PM4/PM0
Please see attached notes for all
abbreviations and acronyms
LOD UnitsMethod
No.
Jones Environmental Laboratory
Kishon Project
David Adams
QF-PM 3.1.2 v10Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 2 of 4
JE Job No.:
SOILS
DEVIATING SAMPLES
SURROGATES
NOTE
JE Job No.:
#
B
DR
M
NA
NAD
ND
NDP
SS
SV
W
+
++
*
CO
OC
NFD
Calibrated against a single substance.
No Determination Possible
ABBREVIATIONS and ACRONYMS USED
No Asbestos Detected.
None Detected (usually refers to VOC and/SVOC TICs).
UKAS accredited.
If you have not already done so, please send us a purchase order if this is required by your company.
All analysis is reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected. Samples are dried at 35°C ±5°C unless
otherwise stated. Moisture content for CEN Leachate tests are dried at 105°C ±5°C.
Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.
Where a CEN 10:1 ZERO Headspace VOC test has been carried out, a 10:1 ratio of water to wet (as received) soil has been used.
No Fibres Detected
Result outside calibration range, results should be considered as indicative only and are not accredited.
Results expressed on as received basis.
Surrogate recovery outside performance criteria. This may be due to a matrix effect.
Data is only accredited when all the requirements of our Quality System have been met. In certain circumstances where the requirements have not
been met, the laboratory may issue the data in an interim report but will remove the accreditation, in this instance results should be considered
indicative only. Where possible samples will be re-extracted and a final report issued with accredited results. Please do not hesitate to contact the
laboratory if further details are required of the circumstances which have led to the removal of accreditation.
Dilution required.
Indicates analyte found in associated method blank.
Not applicable
MCERTS accredited.
AQC failure, accreditation has been removed from this result, if appropriate, see 'Note' on previous page.
Surrogate compounds are added during the preparation process to monitor recovery of analytes. However low recovery in soils is often due to peat,
clay or other organic rich matrices. For waters this can be due to oxidants, surfactants, organic rich sediments or remediation fluids. Acceptable
limits for most organic methods are 70 - 130% and for VOCs are 50 - 150%. When surrogate recoveries are outside the performance criteria but the
associated AQC passes this is assumed to be due to matrix effect. Results are not surrogate corrected.
Analysis subcontracted to a Jones Environmental approved laboratory.
Outside Calibration Range
Suspected carry over
NOTES TO ACCOMPANY ALL SCHEDULES AND REPORTS
Please note we are only MCERTS accredited for sand, loam and clay and any other matrix is outside our scope of accreditation.
Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.
15/689
WATERS
15/689
Where an MCERTS report has been requested, you will be notified within 48 hours of any samples that have been identified as being outside our
MCERTS scope. As validation has been performed on clay, sand and loam, only samples that are predominantly these matrices, or combinations of
them will be within our MCERTS scope. If samples are not one of a combination of the above matrices they will not be marked as MCERTS
accredited.
All samples will be discarded one month after the date of reporting, unless we are instructed to the contrary. If we are instructed to keep samples, a
storage charge of £1 (1.5 Euros) per sample per month will be applied until we are asked to dispose of them.
It is assumed that you have taken representative samples on site and require analysis on a representative subsample. Stones will generally be
included unless we are requested to remove them.
UKAS accreditation applies to surface water and groundwater and one other matrix which is analysis specific, any other liquids are outside our
scope of accreditation
As surface waters require different sample preparation to groundwaters the laboratory must be informed of the water type when submitting samples.
Samples must be received in a condition appropriate to the requested analyses. All samples should be submitted to the laboratory in suitable
containers with sufficient ice packs to sustain an appropriate temperature for the requested analysis. If this is not the case you will be informed and
any test results that may be compromised highlighted on your deviating samples report.
Where appropriate please make sure that our detection limits are suitable for your needs, if they are not, please notify us immediately.
Please note we are not a Drinking Water Inspectorate (DWI) Approved Laboratory . It is important that detection limits are carefully considered when
requesting water analysis.
QF-PM 3.1.9 v25Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 3 of 4
JE Job No: 15/689
Test Method No. Description
Prep Method
No. (if
appropriate)
Description UKAS
MCERTS
(soils
only)
Analysis done on
As Received
(AR) or Air Dried
(AD)
Reported on
dry weight
basis
PM4Gravimetric measurement of Natural Moisture Content and % Moisture Content at either
35°C or 105°C. Calculation based on ISO 11465 and BS1377.PM0 No preparation is required.
TM5
In-House method based on USEPA 8015B. Determination of Extractable Petroleum
Hydrocarbons (EPH) in the carbon chain length range of C8-40 by GC-FID. Accredited to
ISO 17025 on soil and water samples and MCERTS (carbon banding only) on soils. All
accreditation is matrix specific.
PM16 Aliphatic/Aromatic fractionation AR Yes
TM5/TM36 TPH CWG by GC-FID PM16 Aliphatic/Aromatic fractionation AR Yes
TM36
In-House method based on USEPA 8015B. Determination of Gasoline Range Organics
(GRO) in the carbon chain range of C5-12 by headspace GC-FID. Accredited to ISO
17025 on soil and water samples and MCERTS accredited (carbon banding only) on
soils. All accreditation is matrix specific.
PM12
In-house method based on USEPA 5021. Preparation of solid and liquid samples for
headspace analysis. Samples are spiked with surrogates to facilitate quantification. ISO
17025 accredited extraction method. All accreditation is matrix specific
AR Yes
Jones Environmental Laboratory Method Code Appendix
QF-PM 3.1.10 v13 Please include all sections of this report if it is reproduced 4 of 4
Ha’Ashlag 27
Haifa
Israel
3295163
Kishon Project
Attention :
Date :
Your reference :
Our reference :
Location :
Date samples received :
Status :
Issue :
David Adams
Haifa
Israel
Registered Address : Unit 3 Deeside Point, Zone 3, Deeside Industrial Park, Deeside, CH5 2UA. UK
Jones Environmental Laboratory
Tel: +972 58 401 0455
One sample were received for analysis on 11th October, 2015. Please find attached our Test Report which should be read with notes at the end of
the report and should include all sections if reproduced. Interpretations and opinions are outside the scope of any accreditation, and all results relate
only to samples supplied.
All analysis is carried out on as received samples and reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected.
Dave Adams
Site Scientist
12th October, 2015
11th October, 2015
Final report
Compiled By:
Test Report 15/691 Batch 1 Schedule A
1
QF-PM 3.1.3 v10Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 1 of 8
QF-PM 3.1.3 v10Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 2 of 8
Client Name: Report : Solid
Reference:
Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub
Contact:
JE Job No.: 15/691
J E Sample No. 1
Sample ID K3786
Depth
COC No / misc VS-101115-L4-1
Containers T
Sample Date 11/10/2015
Sample Type Solid
Batch Number 1
Date of Receipt 11/10/2015
TPH CWG
Aliphatics
>C5-C6 <0.1 <0.1 mg/kg TM36/PM12
>C6-C8 1.6 <0.1 mg/kg TM36/PM12
>C8-C10 2.9 <0.1 mg/kg TM36/PM12
>C10-C12 67.0 <0.2 mg/kg TM5/PM16
>C12-C16 183 <4 mg/kg TM5/PM16
>C16-C21 149 <7 mg/kg TM5/PM16
>C21-C35 507 <7 mg/kg TM5/PM16
>C35-C44 55 <7 mg/kg TM5/PM16
Total aliphatics C5-44 966 <26 mg/kg TM5/TM36/PM16
Aromatics
>C5-EC7 <0.1 <0.1 mg/kg TM36/PM12
>EC7-EC8 <0.1 <0.1 mg/kg TM36/PM12
>EC8-EC10 0.2 <0.1 mg/kg TM36/PM12
>EC10-EC12 <0.2 <0.2 mg/kg TM5/PM16
>EC12-EC16 39 <4 mg/kg TM5/PM16
>EC16-EC21 88 <7 mg/kg TM5/PM16
>EC21-EC35 403 <7 mg/kg TM5/PM16
>EC35-EC44 61 <7 mg/kg TM5/PM16
Total aromatics C5-44 591 <26 mg/kg TM5/TM36/PM16
Total aliphatics and aromatics(C5-44) 1557 <52 mg/kg TM5/TM36/PM16
Natural Moisture Content 96.5 <0.1 % PM4/PM0
Moisture Content 49.1 <0.1 % PM4/PM0
pH 7.38 <0.01 pH units TM19/PM11
Please see attached notes for all
abbreviations and acronyms
LOD UnitsMethod
No.
Jones Environmental Laboratory
Kishon Project
David Adams
QF-PM 3.1.3 v10Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 3 of 7
Client Name: SVOC Report : Solid
Reference:
Location:
Contact:
JE Job No.: 15/691
J E Sample No. 1
Sample ID K3786
Depth
COC No / misc VS-101115-L4-1
Containers T
Sample Date 11/10/2015
Sample Type Solid
Batch Number 1
Date of Receipt 11/10/2015
SVOC MS
Phenols
2-Chlorophenol <0.01 <0.01 mg/kg TM16/PM8
2-Methylphenol <0.01 <0.01 mg/kg TM16/PM8
2-Nitrophenol <0.01 <0.01 mg/kg TM16/PM8
2,4-Dichlorophenol <0.01 <0.01 mg/kg TM16/PM8
2,4-Dimethylphenol <0.01 <0.01 mg/kg TM16/PM8
2,4,5-Trichlorophenol <0.01 <0.01 mg/kg TM16/PM8
2,4,6-Trichlorophenol <0.01 <0.01 mg/kg TM16/PM8
4-Chloro-3-methylphenol <0.01 <0.01 mg/kg TM16/PM8
4-Methylphenol 0.04 <0.01 mg/kg TM16/PM8
4-Nitrophenol <0.01 <0.01 mg/kg TM16/PM8
Pentachlorophenol <0.01 <0.01 mg/kg TM16/PM8
Phenol <0.01 <0.01 mg/kg TM16/PM8
PAHs
2-Chloronaphthalene <0.01 <0.01 mg/kg TM16/PM8
2-Methylnaphthalene 0.04 <0.01 mg/kg TM16/PM8
Naphthalene <0.01 <0.01 mg/kg TM16/PM8
Acenaphthylene <0.01 <0.01 mg/kg TM16/PM8
Acenaphthene <0.01 <0.01 mg/kg TM16/PM8
Fluorene <0.01 <0.01 mg/kg TM16/PM8
Phenanthrene 0.05 <0.01 mg/kg TM16/PM8
Anthracene <0.01 <0.01 mg/kg TM16/PM8
Fluoranthene <0.01 <0.01 mg/kg TM16/PM8
Pyrene 0.02 <0.01 mg/kg TM16/PM8
Benzo(a)anthracene <0.01 <0.01 mg/kg TM16/PM8
Chrysene <0.01 <0.01 mg/kg TM16/PM8
Benzo(bk)fluoranthene <0.01 <0.01 mg/kg TM16/PM8
Benzo(a)pyrene <0.01 <0.01 mg/kg TM16/PM8
Indeno(123cd)pyrene <0.01 <0.01 mg/kg TM16/PM8
Dibenzo(ah)anthracene <0.01 <0.01 mg/kg TM16/PM8
Benzo(ghi)perylene <0.01 <0.01 mg/kg TM16/PM8
Phthalates
Bis(2-ethylhexyl) phthalate 1.52 <0.01 mg/kg TM16/PM8
Butylbenzyl phthalate <0.01 <0.01 mg/kg TM16/PM8
Di-n-butyl phthalate <0.01 <0.01 mg/kg TM16/PM8
Di-n-Octyl phthalate <0.01 <0.01 mg/kg TM16/PM8
Diethyl phthalate <0.01 <0.01 mg/kg TM16/PM8
Dimethyl phthalate <0.01 <0.01 mg/kg TM16/PM8
Jones Environmental Laboratory
Kishon Project
David Adams
Please see attached notes for all
abbreviations and acronyms
LOD UnitsMethod
No.
QF-PM 3.1.3 v10Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 4 of 7
Client Name: SVOC Report : Solid
Reference:
Location:
Contact:
JE Job No.: 15/691
J E Sample No. 1
Sample ID K3786
Depth
COC No / misc VS-101115-L4-1
Containers T
Sample Date 11/10/2015
Sample Type Solid
Batch Number 1
Date of Receipt 11/10/2015
SVOC MS
Other SVOCs
1,2-Dichlorobenzene <0.01 <0.01 mg/kg TM16/PM8
1,2,4-Trichlorobenzene <0.01 <0.01 mg/kg TM16/PM8
1,3-Dichlorobenzene <0.01 <0.01 mg/kg TM16/PM8
1,4-Dichlorobenzene <0.01 <0.01 mg/kg TM16/PM8
2-Nitroaniline <0.01 <0.01 mg/kg TM16/PM8
2,4-Dinitrotoluene <0.01 <0.01 mg/kg TM16/PM8
2,6-Dinitrotoluene <0.01 <0.01 mg/kg TM16/PM8
3-Nitroaniline <0.01 <0.01 mg/kg TM16/PM8
4-Bromophenylphenylether <0.01 <0.01 mg/kg TM16/PM8
4-Chloroaniline <0.01 <0.01 mg/kg TM16/PM8
4-Chlorophenylphenylether <0.01 <0.01 mg/kg TM16/PM8
4-Nitroaniline <0.01 <0.01 mg/kg TM16/PM8
Azobenzene <0.01 <0.01 mg/kg TM16/PM8
Bis(2-chloroethoxy)methane <0.01 <0.01 mg/kg TM16/PM8
Bis(2-chloroethyl)ether <0.01 <0.01 mg/kg TM16/PM8
Carbazole <0.01 <0.01 mg/kg TM16/PM8
Dibenzofuran <0.01 <0.01 mg/kg TM16/PM8
Hexachlorobenzene <0.01 <0.01 mg/kg TM16/PM8
Hexachlorobutadiene <0.01 <0.01 mg/kg TM16/PM8
Hexachlorocyclopentadiene <0.01 <0.01 mg/kg TM16/PM8
Hexachloroethane <0.01 <0.01 mg/kg TM16/PM8
Isophorone <0.01 <0.01 mg/kg TM16/PM8
N-nitrosodi-n-propylamine <0.01 <0.01 mg/kg TM16/PM8
Nitrobenzene <0.01 <0.01 mg/kg TM16/PM8
LOD UnitsMethod
No.
Jones Environmental Laboratory
Kishon Project
David Adams
Please see attached notes for all
abbreviations and acronyms
QF-PM 3.1.3 v10Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 5 of 7
Client Name: VOC Report : Solid
Reference:
Location:
Contact:
JE Job No.: 15/691
J E Sample No. 1
Sample ID K3786
Depth
COC No / misc VS-101115-L4-1
Containers T
Sample Date 11/10/2015
Sample Type Solid
Batch Number 1
Date of Receipt 11/10/2015
VOC MS
Dichlorodifluoromethane <0.002 <0.002 mg/kg TM15/PM10
Methyl Tertiary Butyl Ether <0.002 <0.002 mg/kg TM15/PM10
Chloromethane <0.003 <0.003 mg/kg TM15/PM10
Vinyl Chloride <0.002 <0.002 mg/kg TM15/PM10
Bromomethane <0.001 <0.001 mg/kg TM15/PM10
Chloroethane <0.002 <0.002 mg/kg TM15/PM10
Trichlorofluoromethane <0.002 <0.002 mg/kg TM15/PM10
1,1-Dichloroethene (1,1 DCE) <0.006 <0.006 mg/kg TM15/PM10
Dichloromethane (DCM) <0.007 <0.007 mg/kg TM15/PM10
trans-1-2-Dichloroethene <0.003 <0.003 mg/kg TM15/PM10
1,1-Dichloroethane <0.003 <0.003 mg/kg TM15/PM10
cis-1-2-Dichloroethene <0.003 <0.003 mg/kg TM15/PM10
2,2-Dichloropropane <0.004 <0.004 mg/kg TM15/PM10
Bromochloromethane <0.003 <0.003 mg/kg TM15/PM10
Chloroform <0.003 <0.003 mg/kg TM15/PM10
1,1,1-Trichloroethane <0.003 <0.003 mg/kg TM15/PM10
1,1-Dichloropropene <0.003 <0.003 mg/kg TM15/PM10
Carbon tetrachloride <0.004 <0.004 mg/kg TM15/PM10
1,2-Dichloroethane <0.004 <0.004 mg/kg TM15/PM10
Benzene <0.003 <0.003 mg/kg TM15/PM10
Trichloroethene (TCE) <0.003 <0.003 mg/kg TM15/PM10
1,2-Dichloropropane <0.006 <0.006 mg/kg TM15/PM10
Dibromomethane <0.003 <0.003 mg/kg TM15/PM10
Bromodichloromethane <0.003 <0.003 mg/kg TM15/PM10
cis-1-3-Dichloropropene <0.004 <0.004 mg/kg TM15/PM10
Toluene <0.003 <0.003 mg/kg TM15/PM10
trans-1-3-Dichloropropene <0.003 <0.003 mg/kg TM15/PM10
1,1,2-Trichloroethane <0.003 <0.003 mg/kg TM15/PM10
Tetrachloroethene (PCE) <0.003 <0.003 mg/kg TM15/PM10
1,3-Dichloropropane <0.003 <0.003 mg/kg TM15/PM10
Dibromochloromethane <0.003 <0.003 mg/kg TM15/PM10
1,2-Dibromoethane <0.003 <0.003 mg/kg TM15/PM10
Chlorobenzene <0.003 <0.003 mg/kg TM15/PM10
1,1,1,2-Tetrachloroethane <0.003 <0.003 mg/kg TM15/PM10
Ethylbenzene 0.041 <0.003 mg/kg TM15/PM10
p/m-Xylene 0.059 <0.006 mg/kg TM15/PM10
o-Xylene 0.024 <0.003 mg/kg TM15/PM10
Styrene <0.003 <0.003 mg/kg TM15/PM10
Bromoform <0.003 <0.003 mg/kg TM15/PM10
Isopropylbenzene 0.022 <0.003 mg/kg TM15/PM10
1,1,2,2-Tetrachloroethane <0.003 <0.003 mg/kg TM15/PM10
Bromobenzene <0.002 <0.002 mg/kg TM15/PM10
1,2,3-Trichloropropane <0.004 <0.004 mg/kg TM15/PM10
Propylbenzene <0.004 <0.004 mg/kg TM15/PM10
2-Chlorotoluene <0.003 <0.003 mg/kg TM15/PM10
1,3,5-Trimethylbenzene <0.003 <0.003 mg/kg TM15/PM10
4-Chlorotoluene <0.003 <0.003 mg/kg TM15/PM10
tert-Butylbenzene <0.005 <0.005 mg/kg TM15/PM10
1,2,4-Trimethylbenzene 0.110 <0.006 mg/kg TM15/PM10
sec-Butylbenzene <0.004 <0.004 mg/kg TM15/PM10
4-Isopropyltoluene 0.108 <0.004 mg/kg TM15/PM10
1,3-Dichlorobenzene <0.004 <0.004 mg/kg TM15/PM10
1,4-Dichlorobenzene <0.004 <0.004 mg/kg TM15/PM10
n-Butylbenzene 0.116 <0.004 mg/kg TM15/PM10
1,2-Dichlorobenzene <0.004 <0.004 mg/kg TM15/PM10
1,2-Dibromo-3-chloropropane <0.004 <0.004 mg/kg TM15/PM10
1,2,4-Trichlorobenzene <0.007 <0.007 mg/kg TM15/PM10
Hexachlorobutadiene <0.004 <0.004 mg/kg TM15/PM10
Naphthalene <0.027 <0.027 mg/kg TM15/PM10
1,2,3-Trichlorobenzene <0.007 <0.007 mg/kg TM15/PM10
Surrogate Recovery Toluene D8 72 <0 % TM15/PM10
Surrogate Recovery 4-Bromofluorobenzene 36 <0 % TM15/PM10
Please see attached notes for all
abbreviations and acronyms
LOD UnitsMethod
No.
Jones Environmental Laboratory
Kishon Project
David Adams
QF-PM 3.1.4 v10Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 6 of 7
JE Job No.:
SOILS
DEVIATING SAMPLES
SURROGATES
NOTE
JE Job No.:
#
B
DR
M
NA
NAD
ND
NDP
SS
SV
W
+
++
*
CO
OC
NFD
Calibrated against a single substance.
No Determination Possible
ABBREVIATIONS and ACRONYMS USED
No Asbestos Detected.
None Detected (usually refers to VOC and/SVOC TICs).
UKAS accredited.
If you have not already done so, please send us a purchase order if this is required by your company.
All analysis is reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected. Samples are dried at 35°C ±5°C unless
otherwise stated. Moisture content for CEN Leachate tests are dried at 105°C ±5°C.
Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.
Where a CEN 10:1 ZERO Headspace VOC test has been carried out, a 10:1 ratio of water to wet (as received) soil has been used.
No Fibres Detected
Result outside calibration range, results should be considered as indicative only and are not accredited.
Results expressed on as received basis.
Surrogate recovery outside performance criteria. This may be due to a matrix effect.
Data is only accredited when all the requirements of our Quality System have been met. In certain circumstances where the requirements have not
been met, the laboratory may issue the data in an interim report but will remove the accreditation, in this instance results should be considered
indicative only. Where possible samples will be re-extracted and a final report issued with accredited results. Please do not hesitate to contact the
laboratory if further details are required of the circumstances which have led to the removal of accreditation.
Dilution required.
Indicates analyte found in associated method blank.
Not applicable
MCERTS accredited.
AQC failure, accreditation has been removed from this result, if appropriate, see 'Note' on previous page.
Surrogate compounds are added during the preparation process to monitor recovery of analytes. However low recovery in soils is often due to peat,
clay or other organic rich matrices. For waters this can be due to oxidants, surfactants, organic rich sediments or remediation fluids. Acceptable
limits for most organic methods are 70 - 130% and for VOCs are 50 - 150%. When surrogate recoveries are outside the performance criteria but the
associated AQC passes this is assumed to be due to matrix effect. Results are not surrogate corrected.
Analysis subcontracted to a Jones Environmental approved laboratory.
Outside Calibration Range
Suspected carry over
NOTES TO ACCOMPANY ALL SCHEDULES AND REPORTS
Please note we are only MCERTS accredited for sand, loam and clay and any other matrix is outside our scope of accreditation.
Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.
15/691
WATERS
15/691
Where an MCERTS report has been requested, you will be notified within 48 hours of any samples that have been identified as being outside our
MCERTS scope. As validation has been performed on clay, sand and loam, only samples that are predominantly these matrices, or combinations of
them will be within our MCERTS scope. If samples are not one of a combination of the above matrices they will not be marked as MCERTS
accredited.
All samples will be discarded one month after the date of reporting, unless we are instructed to the contrary. If we are instructed to keep samples, a
storage charge of £1 (1.5 Euros) per sample per month will be applied until we are asked to dispose of them.
It is assumed that you have taken representative samples on site and require analysis on a representative subsample. Stones will generally be
included unless we are requested to remove them.
UKAS accreditation applies to surface water and groundwater and one other matrix which is analysis specific, any other liquids are outside our
scope of accreditation
As surface waters require different sample preparation to groundwaters the laboratory must be informed of the water type when submitting samples.
Samples must be received in a condition appropriate to the requested analyses. All samples should be submitted to the laboratory in suitable
containers with sufficient ice packs to sustain an appropriate temperature for the requested analysis. If this is not the case you will be informed and
any test results that may be compromised highlighted on your deviating samples report.
Where appropriate please make sure that our detection limits are suitable for your needs, if they are not, please notify us immediately.
Please note we are not a Drinking Water Inspectorate (DWI) Approved Laboratory . It is important that detection limits are carefully considered when
requesting water analysis.
QF-PM 3.1.9 v25Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 7 of 7
Ha’Ashlag 27
Haifa
Israel
3295163
Kishon Project
Attention :
Date :
Your reference :
Our reference :
Location :
Date samples received :
Status :
Issue :
Three samples were received for analysis on 13th October, 2015. Please find attached our Test Report which should be read with notes at the end
of the report and should include all sections if reproduced. Interpretations and opinions are outside the scope of any accreditation, and all results
relate only to samples supplied.
All analysis is carried out on as received samples and reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected.
Dave Adams
Site Scientist
18th October, 2015
13th October, 2015
Final report
Compiled By:
Test Report 15/692 Batch 1 Schedule A
1
David Adams
Haifa
Israel
Registered Address : Unit 3 Deeside Point, Zone 3, Deeside Industrial Park, Deeside, CH5 2UA. UK
Jones Environmental Laboratory
Tel: +972 58 401 0455
QF-PM 3.1.1 v15Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 1 of 7
Client Name: Report : Solid
Reference:
Location: Solids: V=60g VOC jar, J=250g glass jar, T=plastic tub
Contact:
JE Job No.: 15/692
J E Sample No. 1 2 3
Sample ID K3787 K3788-1 K3788-2
Depth
COC No / misc VS-101215-L4-1 VS-101315-L4-1 VS-101315-L4-1
Containers T T T
Sample Date 13/10/2015 13/10/2015 13/10/2015
Sample Type Solid Solid Solid
Batch Number 1 1 1
Date of Receipt 13/10/2015 13/10/2015 13/10/2015
TPH CWG
Aliphatics
>C5-C6 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12
>C6-C8 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12
>C8-C10 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12
>C10-C12 <0.2 0.9 <0.2 <0.2 mg/kg TM5/PM16
>C12-C16 <4 26 19 <4 mg/kg TM5/PM16
>C16-C21 <7 86 64 <7 mg/kg TM5/PM16
>C21-C35 35 207 157 <7 mg/kg TM5/PM16
>C35-C44 <7 30 23 <7 mg/kg TM5/PM16
Total aliphatics C5-44 35 350 263 <26 mg/kg TM5/TM36/PM16
Aromatics
>C5-EC7 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12
>EC7-EC8 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12
>EC8-EC10 <0.1 <0.1 <0.1 <0.1 mg/kg TM36/PM12
>EC10-EC12 <0.2 <0.2 <0.2 <0.2 mg/kg TM5/PM16
>EC12-EC16 <4 <4 <4 <4 mg/kg TM5/PM16
>EC16-EC21 <7 21 20 <7 mg/kg TM5/PM16
>EC21-EC35 36 117 121 <7 mg/kg TM5/PM16
>EC35-EC44 <7 18 25 <7 mg/kg TM5/PM16
Total aromatics C5-44 36 156 166 <26 mg/kg TM5/TM36/PM16
Total aliphatics and aromatics(C5-44) 71 506 429 <52 mg/kg TM5/TM36/PM16
Natural Moisture Content 19.7 17.2 17.2 <0.1 % PM4/PM0
Moisture Content 16.4 14.7 14.7 <0.1 % PM4/PM0
pH 8.03 7.81 7.76 <0.01 pH units TM19/PM11
Please see attached notes for all
abbreviations and acronyms
LOD UnitsMethod
No.
Jones Environmental Laboratory
Kishon Project
David Adams
QF-PM 3.1.2 v10Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 2 of 7
Client Name: SVOC Report : Solid
Reference:
Location:
Contact:
JE Job No.: 15/692
J E Sample No. 1 2 3
Sample ID K3787 K3788-1 K3788-2
Depth
COC No / misc VS-101215-L4-1 VS-101315-L4-1 VS-101315-L4-1
Containers T T T
Sample Date 13/10/2015 13/10/2015 13/10/2015
Sample Type Solid Solid Solid
Batch Number 1 1 1
Date of Receipt 13/10/2015 13/10/2015 13/10/2015
SVOC MS
Phenols
2-Chlorophenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
2-Methylphenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
2-Nitrophenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
2,4-Dichlorophenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
2,4-Dimethylphenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
2,4,5-Trichlorophenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
2,4,6-Trichlorophenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
4-Chloro-3-methylphenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
4-Methylphenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
4-Nitrophenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Pentachlorophenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Phenol <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
PAHs
2-Chloronaphthalene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
2-Methylnaphthalene <0.01 <0.01 0.01 <0.01 mg/kg TM16/PM8
Naphthalene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Acenaphthylene <0.01 <0.01 0.02 <0.01 mg/kg TM16/PM8
Acenaphthene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Fluorene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Phenanthrene <0.01 0.02 0.03 <0.01 mg/kg TM16/PM8
Anthracene <0.01 <0.01 0.01 <0.01 mg/kg TM16/PM8
Fluoranthene <0.01 0.02 0.02 <0.01 mg/kg TM16/PM8
Pyrene 0.02 0.04 0.05 <0.01 mg/kg TM16/PM8
Benzo(a)anthracene 0.05 0.03 0.04 <0.01 mg/kg TM16/PM8
Chrysene <0.01 0.03 0.04 <0.01 mg/kg TM16/PM8
Benzo(bk)fluoranthene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Benzo(a)pyrene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Indeno(123cd)pyrene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Dibenzo(ah)anthracene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Benzo(ghi)perylene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Phthalates
Bis(2-ethylhexyl) phthalate <0.01 1.11 1.34 <0.01 mg/kg TM16/PM8
Butylbenzyl phthalate <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Di-n-butyl phthalate <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Di-n-Octyl phthalate <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Diethyl phthalate <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Dimethyl phthalate <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Please see attached notes for all
abbreviations and acronyms
LOD UnitsMethod
No.
Jones Environmental Laboratory
Kishon Project
David Adams
QF-PM 3.1.3 v10Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 3 of 7
Client Name: SVOC Report : Solid
Reference:
Location:
Contact:
JE Job No.: 15/692
J E Sample No. 1 2 3
Sample ID K3787 K3788-1 K3788-2
Depth
COC No / misc VS-101215-L4-1 VS-101315-L4-1 VS-101315-L4-1
Containers T T T
Sample Date 13/10/2015 13/10/2015 13/10/2015
Sample Type Solid Solid Solid
Batch Number 1 1 1
Date of Receipt 13/10/2015 13/10/2015 13/10/2015
SVOC MS
Other SVOCs
1,2-Dichlorobenzene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
1,2,4-Trichlorobenzene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
1,3-Dichlorobenzene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
1,4-Dichlorobenzene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
2-Nitroaniline <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
2,4-Dinitrotoluene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
2,6-Dinitrotoluene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
3-Nitroaniline <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
4-Bromophenylphenylether <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
4-Chloroaniline <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
4-Chlorophenylphenylether <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
4-Nitroaniline <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Azobenzene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Bis(2-chloroethoxy)methane <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Bis(2-chloroethyl)ether <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Carbazole <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Dibenzofuran <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Hexachlorobenzene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Hexachlorobutadiene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Hexachlorocyclopentadiene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Hexachloroethane <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Isophorone <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
N-nitrosodi-n-propylamine <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
Nitrobenzene <0.01 <0.01 <0.01 <0.01 mg/kg TM16/PM8
LOD UnitsMethod
No.
Jones Environmental Laboratory
Kishon Project
David Adams
Please see attached notes for all
abbreviations and acronyms
QF-PM 3.1.3 v10Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 4 of 7
Client Name: VOC Report : Solid
Reference:
Location:
Contact:
JE Job No.: 15/692
J E Sample No. 1 2 3
Sample ID K3787 K3788-1 K3788-2
Depth
COC No / misc VS-101215-L4-1 VS-101315-L4-1 VS-101315-L4-1
Containers T T T
Sample Date 13/10/2015 13/10/2015 13/10/2015
Sample Type Solid Solid Solid
Batch Number 1 1 1
Date of Receipt 13/10/2015 13/10/2015 13/10/2015
VOC MS
Dichlorodifluoromethane <0.002 <0.002 <0.002 <0.002 mg/kg TM15/PM10
Methyl Tertiary Butyl Ether <0.002 <0.002 <0.002 <0.002 mg/kg TM15/PM10
Chloromethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
Vinyl Chloride <0.002 <0.002 <0.002 <0.002 mg/kg TM15/PM10
Bromomethane <0.001 <0.001 <0.001 <0.001 mg/kg TM15/PM10
Chloroethane <0.002 <0.002 <0.002 <0.002 mg/kg TM15/PM10
Trichlorofluoromethane <0.002 <0.002 <0.002 <0.002 mg/kg TM15/PM10
1,1-Dichloroethene (1,1 DCE) <0.006 <0.006 <0.006 <0.006 mg/kg TM15/PM10
Dichloromethane (DCM) <0.007 <0.007 <0.007 <0.007 mg/kg TM15/PM10
trans-1-2-Dichloroethene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
1,1-Dichloroethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
cis-1-2-Dichloroethene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
2,2-Dichloropropane <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10
Bromochloromethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
Chloroform <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
1,1,1-Trichloroethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
1,1-Dichloropropene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
Carbon tetrachloride <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10
1,2-Dichloroethane <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10
Benzene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
Trichloroethene (TCE) <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
1,2-Dichloropropane <0.006 <0.006 <0.006 <0.006 mg/kg TM15/PM10
Dibromomethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
Bromodichloromethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
cis-1-3-Dichloropropene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10
Toluene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
trans-1-3-Dichloropropene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
1,1,2-Trichloroethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
Tetrachloroethene (PCE) <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
1,3-Dichloropropane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
Dibromochloromethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
1,2-Dibromoethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
Chlorobenzene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
1,1,1,2-Tetrachloroethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
Ethylbenzene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
p/m-Xylene <0.006 <0.006 <0.006 <0.006 mg/kg TM15/PM10
o-Xylene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
Styrene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
Bromoform <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
Isopropylbenzene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
1,1,2,2-Tetrachloroethane <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
Bromobenzene <0.002 <0.002 <0.002 <0.002 mg/kg TM15/PM10
1,2,3-Trichloropropane <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10
Propylbenzene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10
2-Chlorotoluene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
1,3,5-Trimethylbenzene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
4-Chlorotoluene <0.003 <0.003 <0.003 <0.003 mg/kg TM15/PM10
tert-Butylbenzene <0.005 <0.005 <0.005 <0.005 mg/kg TM15/PM10
1,2,4-Trimethylbenzene <0.006 <0.006 <0.006 <0.006 mg/kg TM15/PM10
sec-Butylbenzene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10
4-Isopropyltoluene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10
1,3-Dichlorobenzene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10
1,4-Dichlorobenzene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10
n-Butylbenzene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10
1,2-Dichlorobenzene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10
1,2-Dibromo-3-chloropropane <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10
1,2,4-Trichlorobenzene <0.007 <0.007 <0.007 <0.007 mg/kg TM15/PM10
Hexachlorobutadiene <0.004 <0.004 <0.004 <0.004 mg/kg TM15/PM10
Naphthalene <0.027 <0.027 <0.027 <0.027 mg/kg TM15/PM10
1,2,3-Trichlorobenzene <0.007 <0.007 <0.007 <0.007 mg/kg TM15/PM10
Surrogate Recovery Toluene D8 108 103 96 <0 % TM15/PM10
Surrogate Recovery 4-Bromofluorobenzene 92 77 65 <0 % TM15/PM10
Please see attached notes for all
abbreviations and acronyms
LOD UnitsMethod
No.
Jones Environmental Laboratory
Kishon Project
David Adams
QF-PM 3.1.4 v10Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 5 of 7
JE Job No.:
SOILS
DEVIATING SAMPLES
SURROGATES
NOTE
JE Job No.:
#
B
DR
M
NA
NAD
ND
NDP
SS
SV
W
+
++
*
CO
OC
NFD
Outside Calibration Range
Suspected carry over
NOTES TO ACCOMPANY ALL SCHEDULES AND REPORTS
Please note we are only MCERTS accredited for sand, loam and clay and any other matrix is outside our scope of accreditation.
Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.
15/692
WATERS
15/692
Where an MCERTS report has been requested, you will be notified within 48 hours of any samples that have been identified as being outside our
MCERTS scope. As validation has been performed on clay, sand and loam, only samples that are predominantly these matrices, or combinations of
them will be within our MCERTS scope. If samples are not one of a combination of the above matrices they will not be marked as MCERTS
accredited.
All samples will be discarded one month after the date of reporting, unless we are instructed to the contrary. If we are instructed to keep samples, a
storage charge of £1 (1.5 Euros) per sample per month will be applied until we are asked to dispose of them.
It is assumed that you have taken representative samples on site and require analysis on a representative subsample. Stones will generally be
included unless we are requested to remove them.
UKAS accreditation applies to surface water and groundwater and one other matrix which is analysis specific, any other liquids are outside our
scope of accreditation
As surface waters require different sample preparation to groundwaters the laboratory must be informed of the water type when submitting samples.
Samples must be received in a condition appropriate to the requested analyses. All samples should be submitted to the laboratory in suitable
containers with sufficient ice packs to sustain an appropriate temperature for the requested analysis. If this is not the case you will be informed and
any test results that may be compromised highlighted on your deviating samples report.
Where appropriate please make sure that our detection limits are suitable for your needs, if they are not, please notify us immediately.
Please note we are not a Drinking Water Inspectorate (DWI) Approved Laboratory . It is important that detection limits are carefully considered when
requesting water analysis.
If you have not already done so, please send us a purchase order if this is required by your company.
All analysis is reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected. Samples are dried at 35°C ±5°C unless
otherwise stated. Moisture content for CEN Leachate tests are dried at 105°C ±5°C.
Where Mineral Oil or Fats, Oils and Grease is quoted, this refers to Total Aliphatics C10-C40.
Where a CEN 10:1 ZERO Headspace VOC test has been carried out, a 10:1 ratio of water to wet (as received) soil has been used.
No Fibres Detected
Result outside calibration range, results should be considered as indicative only and are not accredited.
Results expressed on as received basis.
Surrogate recovery outside performance criteria. This may be due to a matrix effect.
Data is only accredited when all the requirements of our Quality System have been met. In certain circumstances where the requirements have not
been met, the laboratory may issue the data in an interim report but will remove the accreditation, in this instance results should be considered
indicative only. Where possible samples will be re-extracted and a final report issued with accredited results. Please do not hesitate to contact the
laboratory if further details are required of the circumstances which have led to the removal of accreditation.
Dilution required.
Indicates analyte found in associated method blank.
Not applicable
MCERTS accredited.
AQC failure, accreditation has been removed from this result, if appropriate, see 'Note' on previous page.
Surrogate compounds are added during the preparation process to monitor recovery of analytes. However low recovery in soils is often due to peat,
clay or other organic rich matrices. For waters this can be due to oxidants, surfactants, organic rich sediments or remediation fluids. Acceptable
limits for most organic methods are 70 - 130% and for VOCs are 50 - 150%. When surrogate recoveries are outside the performance criteria but the
associated AQC passes this is assumed to be due to matrix effect. Results are not surrogate corrected.
Analysis subcontracted to a Jones Environmental approved laboratory.
Calibrated against a single substance.
No Determination Possible
ABBREVIATIONS and ACRONYMS USED
No Asbestos Detected.
None Detected (usually refers to VOC and/SVOC TICs).
UKAS accredited.
QF-PM 3.1.9 v25Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 6 of 7
JE Job No: 15/692
Test Method No. Description
Prep Method
No. (if
appropriate)
Description UKAS
MCERTS
(soils
only)
Analysis done on
As Received
(AR) or Air Dried
(AD)
Reported on
dry weight
basis
PM4Gravimetric measurement of Natural Moisture Content and % Moisture Content at either
35°C or 105°C. Calculation based on ISO 11465 and BS1377.PM0 No preparation is required.
TM5
In-House method based on USEPA 8015B. Determination of Extractable Petroleum
Hydrocarbons (EPH) in the carbon chain length range of C8-40 by GC-FID. Accredited to
ISO 17025 on soil and water samples and MCERTS (carbon banding only) on soils. All
accreditation is matrix specific.
PM16 Aliphatic/Aromatic fractionation AR Yes
TM5/TM36 TPH CWG by GC-FID PM16 Aliphatic/Aromatic fractionation AR Yes
TM15
In-House method based on USEPA 8260. Determination of Volatile Organic compounds
(VOCs) by Headspace GC-MS. Accredited to ISO 17025 for soils and waters and
MCERTS for Soils. All accreditation is matrix specific. Quantification by Internal Standard
method.
PM10
In-house method based on USEPA 5021. Preparation of solid and liquid samples for
headspace analysis. Samples are spiked with surrogates to facilitate quantification. ISO
17025 accredited extraction method. All accreditation is matrix specific
AR Yes
TM16
In-House method based on USEPA 8270. Determination of Semi-Volatile Organic
compounds (SVOCs) by GC-MS. Accredited to ISO 17025 for waters. All accreditation is
matrix specific. Quantification by Internal Standard method.
PM8In-house method based on USEPA 3510. ISO 17025 accredited extraction method for
organic extraction from solid samples using an end over end agitator.AR Yes
TM19 pH by meter PM11 1:2.5 soil/water extraction AR No
TM36
In-House method based on USEPA 8015B. Determination of Gasoline Range Organics
(GRO) in the carbon chain range of C5-12 by headspace GC-FID. Accredited to ISO
17025 on soil and water samples and MCERTS accredited (carbon banding only) on
soils. All accreditation is matrix specific.
PM12
In-house method based on USEPA 5021. Preparation of solid and liquid samples for
headspace analysis. Samples are spiked with surrogates to facilitate quantification. ISO
17025 accredited extraction method. All accreditation is matrix specific
AR Yes
Jones Environmental Laboratory Method Code Appendix
QF-PM 3.1.10 v13 Please include all sections of this report if it is reproduced 7 of 7
Ha’Ashlag 27
Haifa
Israel
3295163
Kishon Project
Attention :
Date :
Your reference :
Our reference :
Location :
Date samples received :
Status :
Issue :
David Adams
Haifa
Israel
Registered Address : Unit 3 Deeside Point, Zone 3, Deeside Industrial Park, Deeside, CH5 2UA. UK
Jones Environmental Laboratory
Tel: +972 58 401 0455
One sample were received for analysis on 15th October, 2015. Please find attached our Test Report which should be read with notes at the end of
the report and should include all sections if reproduced. Interpretations and opinions are outside the scope of any accreditation, and all results relate
only to samples supplied.
All analysis is carried out on as received samples and reported on a dry weight basis unless stated otherwise. Results are not surrogate corrected.
Dave Adams
Site Scientist
19th October, 2015
15th October, 2015
Final report
Compiled By:
Test Report 15/693 Batch 1
1
QF-PM 3.1.1 v15Please include all sections of this report if it is reproduced
All solid results are expressed on a dry weight basis unless stated otherwise. 1 of 1