PMID-sentid	Pub_year	Sent_text		comp_official_name	comp_offsetprotein_name	organism	prot_offset
29965687-4	2018	The SAD process performed well with an average total nitrogen concentration in the effluent of 6.41 mg L-1 when 30 mg L-1 glucose was added to the effluent sewage at ambient temperature.	Nitrogen	53-61	immunoglobulin kappa variable 1-16	Homo sapiens	103-106	
29417482-5	2018	The results showed that addition of 25 mg L-1 fullerene C60 to urea plant wastewater could increase water uptake and nitrogen recovery of the teak plants.	Nitrogen	117-125	immunoglobulin kappa variable 1-16	Homo sapiens	42-45	
29417482-7	2018	However, addition of 50 mg L-1 fullerene C60 to the wastewater decreased the values for water uptake and nitrogen recovery.	Nitrogen	105-113	immunoglobulin kappa variable 1-16	Homo sapiens	27-30	
29965002-3	2018	For the granules, the highest specific nitrogen removal rate of q(TN)=(17.7+-1.0) mg (g h)-1 was obtained at a DO concentration of 2 mg L-1, while the initial NH4+-N concentration was set at 100 mg L-1.	Nitrogen	39-47	immunoglobulin kappa variable 1-16	Homo sapiens	136-139	
29965002-3	2018	For the granules, the highest specific nitrogen removal rate of q(TN)=(17.7+-1.0) mg (g h)-1 was obtained at a DO concentration of 2 mg L-1, while the initial NH4+-N concentration was set at 100 mg L-1.	Nitrogen	39-47	immunoglobulin kappa variable 1-16	Homo sapiens	198-201	
28387149-5	2018	The ammoniacal nitrogen removal ratio decreased under high organic matter concentration (above 100 mg L-1) and low DO (less than 1 mg L-1) condition.	Nitrogen	15-23	immunoglobulin kappa variable 1-16	Homo sapiens	102-105	
28387149-5	2018	The ammoniacal nitrogen removal ratio decreased under high organic matter concentration (above 100 mg L-1) and low DO (less than 1 mg L-1) condition.	Nitrogen	15-23	immunoglobulin kappa variable 1-16	Homo sapiens	134-137	
29965687-7	2018	In normal and low temperature environments, the SAD process functioned well, and the average total nitrogen concentration of the effluent was 6.54 mg L-1 when 30 mg L-1 sodium propionate was added in the influent sewage.	Nitrogen	99-107	immunoglobulin kappa variable 1-16	Homo sapiens	150-153	
29965687-7	2018	In normal and low temperature environments, the SAD process functioned well, and the average total nitrogen concentration of the effluent was 6.54 mg L-1 when 30 mg L-1 sodium propionate was added in the influent sewage.	Nitrogen	99-107	immunoglobulin kappa variable 1-16	Homo sapiens	165-168	
29965691-7	2018	In the recovery phase, the nitrogen removal performance of the reactor could almost reach its initial level at nZVI=0 mg L-1 during an operation of 20 days due to the fast growth of heterotrophic microbes on the surface of the DGS.	Nitrogen	27-35	immunoglobulin kappa variable 1-16	Homo sapiens	121-124	
29965365-11	2017	Finally, when the concentration of phosphate reached 100 mg L-1, the nitrogen removal efficiency of ANAMMOX was seriously inhibited.	Nitrogen	69-77	immunoglobulin kappa variable 1-16	Homo sapiens	60-63	
29247929-4	2018	However, the photocatalytic fuel cell was still able to perform 37% of decolorization in a slow rate (k = 0.033 h-1) under extremely low dissolved oxygen concentration (approximately 0.2 mg L-1) when nitrogen gas was introduced into the fuel cell throughout the 8 h. However, the change of the UV-Vis spectrum indicates that the intermediates of the dye could not be mineralized under insufficient dissolved oxygen level.	Nitrogen	200-208	immunoglobulin kappa variable 1-16	Homo sapiens	190-193	
29964577-2	2017	The results indicated that when ammonia increased to 1200 mg L-1, the MAAOB still maintained good nitrogen removal capability, though there was a slight inhibitory effect.	Nitrogen	98-106	immunoglobulin kappa variable 1-16	Homo sapiens	61-64	
28808683-2	2017	We report copper-mediated formation of N-unsubstituted aliphatic imines from easily available aliphatic azides using a customized phenanthroline-based ligand (L1*).	Nitrogen	39-40	immunoglobulin kappa variable 1-16	Homo sapiens	159-162	
28477543-11	2017	To prevent phytoplankton blooms with 20 mug L-1 chlorophyll-a throughout Lake Taihu, both phosphorus and nitrogen loads need a nearly 90% reduction.	Nitrogen	105-113	immunoglobulin kappa variable 1-16	Homo sapiens	44-47	
29965215-3	2017	The results showed that when the influent ammonia nitrogen concentration was 917-1540 mg L-1, the residual ammonia nitrogen concentration of 6 mg L-1 can be used as the control parameter to meet the requirements of process stability but the ammonia nitrogen sensor had many problems such as high costs and large errors.	Nitrogen	50-58	immunoglobulin kappa variable 1-16	Homo sapiens	89-92	
29965215-3	2017	The results showed that when the influent ammonia nitrogen concentration was 917-1540 mg L-1, the residual ammonia nitrogen concentration of 6 mg L-1 can be used as the control parameter to meet the requirements of process stability but the ammonia nitrogen sensor had many problems such as high costs and large errors.	Nitrogen	50-58	immunoglobulin kappa variable 1-16	Homo sapiens	146-149	
29965215-3	2017	The results showed that when the influent ammonia nitrogen concentration was 917-1540 mg L-1, the residual ammonia nitrogen concentration of 6 mg L-1 can be used as the control parameter to meet the requirements of process stability but the ammonia nitrogen sensor had many problems such as high costs and large errors.	Nitrogen	115-123	immunoglobulin kappa variable 1-16	Homo sapiens	89-92	
29965215-3	2017	The results showed that when the influent ammonia nitrogen concentration was 917-1540 mg L-1, the residual ammonia nitrogen concentration of 6 mg L-1 can be used as the control parameter to meet the requirements of process stability but the ammonia nitrogen sensor had many problems such as high costs and large errors.	Nitrogen	115-123	immunoglobulin kappa variable 1-16	Homo sapiens	146-149	
28604811-6	2017	Mean concentrations, over 56 sampling events, of total N (TN) and total P (TP) in surface runoff at the outlet pipe were 10.9+-6.34 and 1.3+-1.03 mg L-1, respectively.	Nitrogen	55-56	immunoglobulin kappa variable 1-16	Homo sapiens	149-152	
27249226-4	2017	The results showed that the concentration of ammonia nitrogen in wastewater could be reduced from 120.2 to 6.0 mg L-1, and manganese could be simultaneously removed from 302.4 to 1.5 mg L-1 at initial pH of 8.0, the mole ratios of nitrite and ammonia nitrogen of 1.5:1, and voltage of 20 V direct current electrolysis for 4.0 h. XRD analysis showed that manganese dioxide was deposited on the anode, and manganese was mainly removed in the form of manganese hydroxide precipitation in the cathode chamber.	Nitrogen	53-61	immunoglobulin kappa variable 1-16	Homo sapiens	114-117	
29964510-8	2017	The inflow nutrients loads increased significantly in the summer of the normal year, as a result, total nitrogen increased from 1.00 mg L-1 to 2.06 mg L-1, nitrate increased from 0.19 mg L-1 to 1.28 mg L-1, and total phosphorus increased from 0.023 mg L-1 to 0.088 mg L-1 in the lacustrine zone of the reservoir.	Nitrogen	104-112	immunoglobulin kappa variable 1-16	Homo sapiens	136-139	
29964510-8	2017	The inflow nutrients loads increased significantly in the summer of the normal year, as a result, total nitrogen increased from 1.00 mg L-1 to 2.06 mg L-1, nitrate increased from 0.19 mg L-1 to 1.28 mg L-1, and total phosphorus increased from 0.023 mg L-1 to 0.088 mg L-1 in the lacustrine zone of the reservoir.	Nitrogen	104-112	immunoglobulin kappa variable 1-16	Homo sapiens	151-154	
29964510-8	2017	The inflow nutrients loads increased significantly in the summer of the normal year, as a result, total nitrogen increased from 1.00 mg L-1 to 2.06 mg L-1, nitrate increased from 0.19 mg L-1 to 1.28 mg L-1, and total phosphorus increased from 0.023 mg L-1 to 0.088 mg L-1 in the lacustrine zone of the reservoir.	Nitrogen	104-112	immunoglobulin kappa variable 1-16	Homo sapiens	151-154	
29964510-8	2017	The inflow nutrients loads increased significantly in the summer of the normal year, as a result, total nitrogen increased from 1.00 mg L-1 to 2.06 mg L-1, nitrate increased from 0.19 mg L-1 to 1.28 mg L-1, and total phosphorus increased from 0.023 mg L-1 to 0.088 mg L-1 in the lacustrine zone of the reservoir.	Nitrogen	104-112	immunoglobulin kappa variable 1-16	Homo sapiens	151-154	
29964510-8	2017	The inflow nutrients loads increased significantly in the summer of the normal year, as a result, total nitrogen increased from 1.00 mg L-1 to 2.06 mg L-1, nitrate increased from 0.19 mg L-1 to 1.28 mg L-1, and total phosphorus increased from 0.023 mg L-1 to 0.088 mg L-1 in the lacustrine zone of the reservoir.	Nitrogen	104-112	immunoglobulin kappa variable 1-16	Homo sapiens	151-154	
29964510-8	2017	The inflow nutrients loads increased significantly in the summer of the normal year, as a result, total nitrogen increased from 1.00 mg L-1 to 2.06 mg L-1, nitrate increased from 0.19 mg L-1 to 1.28 mg L-1, and total phosphorus increased from 0.023 mg L-1 to 0.088 mg L-1 in the lacustrine zone of the reservoir.	Nitrogen	104-112	immunoglobulin kappa variable 1-16	Homo sapiens	151-154	
29964737-2	2016	The results indicated that when the influent F- concentration was in the range of 0-700 mg L-1, the nitrogen removal efficiency promoted with rising influent F- concentration.	Nitrogen	100-108	immunoglobulin kappa variable 1-16	Homo sapiens	91-94	
29964739-5	2016	Finally, the average effluent total nitrogen concentration was 10 mg L-1, with total nitrogen volume load of ANAMMOX system of 0.36 kg (m3 d)-1.	Nitrogen	36-44	immunoglobulin kappa variable 1-16	Homo sapiens	69-72	
29964739-7	2016	The nitrogen of municipal wastewater could be stable and efficiently removed by the shortcut nitrification -ANAMMOX integration ABR with temperature of 30C and dissolved oxygen of 1-2 mg L-1.	Nitrogen	4-12	immunoglobulin kappa variable 1-16	Homo sapiens	187-190	
29964741-4	2016	The results showed that a One-stage Autotrophic Nitrogen Removal Process was successfully established in 83 days under the following conditions: temperature at (30+-2)C , pH at 7.8-8.2, dissolved oxygen (DO) at 0.2-1.1mg L-1 and upflow velocity at 2.0-4.0m h-1.	Nitrogen	48-56	immunoglobulin kappa variable 1-16	Homo sapiens	221-224	
25864004-5	2015	Maximum conversion of ammonia to nitrogen at the rates of 0.569 and 0.766 mg L(-1) min(-1) are achieved at low (0.01 M NH4Cl and 0.1 M KOH) and high (0.07 M NH4Cl and 0.15 M KOH) inlet concentrations, respectively.	Nitrogen	33-41	immunoglobulin kappa variable 1-16	Homo sapiens	77-89	
27506043-3	2016	Nitrite nitrogen kept accumulating up to 800 mg   L-1 when the influent COD/TN ratio was 0.8 +- 0.2, and the removal rates of TN, ammonium nitrogen and total organic carbon (TOC) were only 18.3% +- 12.2%, 84.2% +- 10.3% and 60.7% +- 10.7%, respectively.	Nitrogen	8-16	immunoglobulin kappa variable 1-16	Homo sapiens	50-53	
27506043-4	2016	By contrast, as the influent COD/ TN ratio was increased to 2.4 +- 0.5, the accumulated concentration of nitrite nitrogen sharply decreased from 800 mg   L-1 to below 10 mg-L-1, and the removal rates of TN, ammonium nitrogen and TOC were increased to over 90%, 95% and 85%, respectively.	Nitrogen	113-121	immunoglobulin kappa variable 1-16	Homo sapiens	154-157	
27506043-4	2016	By contrast, as the influent COD/ TN ratio was increased to 2.4 +- 0.5, the accumulated concentration of nitrite nitrogen sharply decreased from 800 mg   L-1 to below 10 mg-L-1, and the removal rates of TN, ammonium nitrogen and TOC were increased to over 90%, 95% and 85%, respectively.	Nitrogen	113-121	immunoglobulin kappa variable 1-16	Homo sapiens	173-176	
27548970-6	2016	After 93 d operation, the total nitrogen in effluent was stabilized below 50 mg   L-1, the total nitrogen removal efficiency reached 90%, and the removal rate reached 5 kg   (m3   d)-1.	Nitrogen	32-40	immunoglobulin kappa variable 1-16	Homo sapiens	82-85	
27506019-6	2016	The concentration of the dissolved inorganic nitrogen was higher than 0.30 mg   L-1, and the value of N/P was higher than 60, which indicated that PO43--P was the nutrient limiting phytoplankton growth in the tidal reach and estuary of the Daliao river in August and November, 2013.	Nitrogen	45-53	immunoglobulin kappa variable 1-16	Homo sapiens	80-83	
26077503-8	2015	The average runoff volume was 289 mm (varied from 221 to 357 mm), which contained 15.7 (varied from 3.3 to 39.2 mg L-1) mg L-1 total N.	Nitrogen	133-134	immunoglobulin kappa variable 1-16	Homo sapiens	123-126	
11445959-6	2001	For n-PG, calibration graphs were linear over the range 1.0-300.0 mg L-1 in area and the RSD was between 1.4 and 1.5%.	Nitrogen	4-5	immunoglobulin kappa variable 1-16	Homo sapiens	69-72	
15356719-9	2004	The electronic charge distribution in L(4) and L(5) is similar to that found in other terdentate ligands such as terpyridine which have equally poor extraction properties and suggests that the unique properties of L(1) evolve from the presence of two adjacent nitrogen atoms in the triazine rings.	Nitrogen	260-268	immunoglobulin kappa variable 1-16	Homo sapiens	214-218	
31775099-4	2020	At 200 mg L-1 phenol, 99.8% phenol, 97.5% COD and 89.8% nitrogen could be together removed.	Nitrogen	56-64	immunoglobulin kappa variable 1-16	Homo sapiens	10-13	
31654960-3	2020	Excess N2 in hyporheic porewaters ranged from <0.1 to 8.65 mg L-1 and was significantly higher in porewaters from the 1.3 m (ground water source) versus 0.3 m (mixed surface and ground water) depths.	Nitrogen	7-9	immunoglobulin kappa variable 1-16	Homo sapiens	65-68	
31864635-6	2020	The N-CNTC-coated fiber was then used to identify polychlorinated biphenyls (PCBs) with wide linear range (0.3-1000.0 ng L-1), low limits of detection (0.10-0.22 ng L-1), good repeatability (intra-day, 2.6-3.8%; inter-day, 3.3-4.8%), and good reproducibility (<8.6%).	Nitrogen	4-5	immunoglobulin kappa variable 1-16	Homo sapiens	121-124	
31864635-6	2020	The N-CNTC-coated fiber was then used to identify polychlorinated biphenyls (PCBs) with wide linear range (0.3-1000.0 ng L-1), low limits of detection (0.10-0.22 ng L-1), good repeatability (intra-day, 2.6-3.8%; inter-day, 3.3-4.8%), and good reproducibility (<8.6%).	Nitrogen	4-5	immunoglobulin kappa variable 1-16	Homo sapiens	165-168	
31654960-4	2020	In deep groundwater wells (3-7 m), median excess N2 concentration was 5.39 mg L-1 (range = <0.1-14.6 mg L-1).	Nitrogen	49-51	immunoglobulin kappa variable 1-16	Homo sapiens	78-81	
31854767-4	2019	The results showed that the stabilized sludge dosage was 3%, and the annual average mass concentrations of total nitrogen (TN) and nitrate nitrogen (NO3--N) were 3.27 mg L-1 and 1.61 mg L-1.	Nitrogen	149-155	immunoglobulin kappa variable 1-16	Homo sapiens	170-179	
31150877-4	2019	The results indicated that under long-term exposure to 5 mg L-1 tetracycline and 1 mg L-1 sulfamethoxazole, removals of chemical oxygen demand and total nitrogen were inhibited, the tendency of sludge bulking was increased, more filamentous bacteria were observed and more extracellular polymeric substance was secreted.	Nitrogen	153-161	immunoglobulin kappa variable 1-16	Homo sapiens	60-82	
31150877-4	2019	The results indicated that under long-term exposure to 5 mg L-1 tetracycline and 1 mg L-1 sulfamethoxazole, removals of chemical oxygen demand and total nitrogen were inhibited, the tendency of sludge bulking was increased, more filamentous bacteria were observed and more extracellular polymeric substance was secreted.	Nitrogen	153-161	immunoglobulin kappa variable 1-16	Homo sapiens	60-63	
31628372-4	2019	Biomass concentration was enhanced to 4.1 g L-1 through intermittent feeding of nitrogen source and phosphate.	Nitrogen	80-88	immunoglobulin kappa variable 1-16	Homo sapiens	44-47	
31176936-3	2019	Significantly higher total nitrogen removal efficiency (TNRE) was observed in L1-CDBFT (92.2%) than C1-CDBFT (87.5%, P < 0.05; after day 14).	Nitrogen	27-35	immunoglobulin kappa variable 1-16	Homo sapiens	78-86	
31854767-7	2019	As a result, the concentrations of TN and NO3--N in the effluent were decreased to 2.16 mg L-1 and 1.38 mg L-1, respectively.	Nitrogen	42-48	immunoglobulin kappa variable 1-16	Homo sapiens	91-94	
31854767-7	2019	As a result, the concentrations of TN and NO3--N in the effluent were decreased to 2.16 mg L-1 and 1.38 mg L-1, respectively.	Nitrogen	42-48	immunoglobulin kappa variable 1-16	Homo sapiens	107-110	
30628347-6	2019	The results also suggested that 0.83 mg L-1NO3--N was consumed per 1 mg L-1 PO43--P removed during the denitrifying phosphorus removal, indicating that the simultaneous nitrogen and phosphorus removal was achieved in the ABR-MBR system.	Nitrogen	169-177	immunoglobulin kappa variable 1-16	Homo sapiens	40-43	
31854731-2	2019	The results showed that the nitrogen concentration ranged from 4.43 to 13.83 mg L-1 in four park water bodies, which exhibited notable nitrogen pollution characteristics.	Nitrogen	28-36	immunoglobulin kappa variable 1-16	Homo sapiens	80-83	
31854731-2	2019	The results showed that the nitrogen concentration ranged from 4.43 to 13.83 mg L-1 in four park water bodies, which exhibited notable nitrogen pollution characteristics.	Nitrogen	135-143	immunoglobulin kappa variable 1-16	Homo sapiens	80-83	
31087872-4	2019	The nitrogen removal efficiency was optimum when the COD concentration was between 15.00 and 30.00 mg L-1.	Nitrogen	4-12	immunoglobulin kappa variable 1-16	Homo sapiens	102-105	
31087933-3	2019	The results showed that with an influent total nitrogen (TN) of 40 mg L-1, the optimal HRT of the No.1 reactor was 2.5 h, and the removal rate and effluent concentration of TN were stable at 72.2% and 10.55 mg L-1, respectively.	Nitrogen	47-55	immunoglobulin kappa variable 1-16	Homo sapiens	70-73	
30620788-6	2019	Porous carbon tri-doped with nitrogen, phosphorous, and oxygen exhibits a high packing density (2.13 g cm-3 ) and an exceptional volumetric energy density (36.8 Wh L-1 ) in alkaline electrolytes, making it competitive to even some Ni-MH cells.	Nitrogen	29-37	immunoglobulin kappa variable 1-16	Homo sapiens	164-167	
30743916-3	2019	The mean concentration of total dissolved nitrogen (TDN) in the two catchments was 0.63 mg L-1, which is generally higher than other permafrost catchments around the Arctic Ocean.	Nitrogen	42-50	immunoglobulin kappa variable 1-16	Homo sapiens	91-94	
30628403-4	2018	When the two-stage PN-ANAMMOX process was operated under NH4+-N-limited conditions, the "limit of technology" for nitrogen removal (TN<3 mg L-1) could be easily achieved by following anoxic denitrification.	Nitrogen	114-122	immunoglobulin kappa variable 1-16	Homo sapiens	143-146	
30628296-3	2019	When the ammonia concentration was low, the total nitrogen removal rate in the effluent decreased to 75.3%, the total nitrogen concentration in the effluent was~10 mg L-1, and excessive proliferation of the NOB was observed.	Nitrogen	118-126	immunoglobulin kappa variable 1-16	Homo sapiens	167-170	
30628296-6	2019	When the ammonia concentration was low, the concentration of ammonia nitrogen in effluent was less than 1.0 mg L-1 and the total nitrogen concentration in the effluent was less than 6 mg L-1.	Nitrogen	69-77	immunoglobulin kappa variable 1-16	Homo sapiens	111-114	
30628296-6	2019	When the ammonia concentration was low, the concentration of ammonia nitrogen in effluent was less than 1.0 mg L-1 and the total nitrogen concentration in the effluent was less than 6 mg L-1.	Nitrogen	129-137	immunoglobulin kappa variable 1-16	Homo sapiens	187-190	
30121531-9	2019	At the end of monitoring, regardless of the arriving inflow load, the discharge presented stable concentrations of approximately 30 mg L-1, appearing to indicate that the limits for nitrogen elimination.	Nitrogen	182-190	immunoglobulin kappa variable 1-16	Homo sapiens	135-138	
30628406-4	2018	When the NH4+-N and NO2--N concentrations were 450 mg L-1 and 560 mg L-1, respectively, the nitrogen removal was achieved in both the high-and low-substrate concentration reactors and the maximum NRR was 16.97 kg (m3 d)-1 and 14.43 kg (m3 d)-1, respectively.	Nitrogen	92-100	immunoglobulin kappa variable 1-16	Homo sapiens	54-72	
29998685-4	2018	The nitrogen removal efficiency of the PN/A double-bacteria-layer system remained stable at~80% when the influent NH4+-N was 200 mg L-1 or 400 mg L-1 in the presence of 1.0 mg L-1 DO, whereas those of the control group were only 58.1% and 61.4%, respectively.	Nitrogen	4-12	immunoglobulin kappa variable 1-16	Homo sapiens	146-149	
29998685-4	2018	The nitrogen removal efficiency of the PN/A double-bacteria-layer system remained stable at~80% when the influent NH4+-N was 200 mg L-1 or 400 mg L-1 in the presence of 1.0 mg L-1 DO, whereas those of the control group were only 58.1% and 61.4%, respectively.	Nitrogen	4-12	immunoglobulin kappa variable 1-16	Homo sapiens	146-149	
29709805-4	2018	Furthermore, the nitrogen removal efficiency (NRE) decreased to 82.02 +- 3.14% when COD was increased to 730 +- 9 mg L-1, and effluent free ammonia (FA) reached 21.93 +- 4.71 mg L-1 might be one of factors leading to inhibition.	Nitrogen	17-25	immunoglobulin kappa variable 1-16	Homo sapiens	117-120	
29709805-4	2018	Furthermore, the nitrogen removal efficiency (NRE) decreased to 82.02 +- 3.14% when COD was increased to 730 +- 9 mg L-1, and effluent free ammonia (FA) reached 21.93 +- 4.71 mg L-1 might be one of factors leading to inhibition.	Nitrogen	17-25	immunoglobulin kappa variable 1-16	Homo sapiens	178-181	
29709805-3	2018	Efficient nitrogen removal was realized because denitrifying bacteria and anammox bacteria (AnAOB) had a better synergistic effect under the condition of chemical oxygen demand (COD) concentrations lower than 251 +- 7 mg L-1.	Nitrogen	10-18	immunoglobulin kappa variable 1-16	Homo sapiens	221-224	
29709805-5	2018	However, the nitrogen-removal contribution rate of anammox remained steady at 61.97 +- 2.84% at COD of 730 +- 9 mg L-1, which indicated that anammox was still dominant in the system.	Nitrogen	13-21	immunoglobulin kappa variable 1-16	Homo sapiens	115-118	
29501031-4	2018	The nitrogen removal was suppressed and could recover to the initial level during the same period under 10-20 mg L-1 Fe (II), while it did not recover to the initial level under 30 mg L-1 Fe (II) and showed no recovery performance under 50 mg L-1 Fe (II).	Nitrogen	4-12	immunoglobulin kappa variable 1-16	Homo sapiens	113-116